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OGC Cycle Group Case Group Name Planning Unit County (-ies) WBID Water Segment Name Number

Choctawhatchee - Little Bear Creek (South 3 3 16-0477 St. Andrews Bay Bay, Calhoun 1041 St. Andrew Fork)

Choctawhatchee - 3 3 16-0479 St. Andrews Bay Bay 1061A West Bay St. Andrew

Choctawhatchee - 3 3 16-0478 St. Andrews Bay Bay 1061A West Bay St. Andrew

Choctawhatchee - St Andrews Bay (North 2 3 10-0533 St. Andrews Bay Bay 1061B St. Andrew Segment) Choctawhatchee - 1 3 05-1148 St. Andrews Bay Bay 1061BB Carl Gray Park St. Andrew Choctawhatchee - 1 3 05-1150 St. Andrews Bay Bay 1061CB Beach Drive St. Andrew

Choctawhatchee - 3 3 16-0480 St. Andrews Bay Bay 1061E St Andrew Bay (Mouth) St. Andrew

Choctawhatchee - 1 3 05-1151 St. Andrews Bay Bay 1061EB Delwood St. Andrew

Choctawhatchee - 1 3 05-1152 St. Andrews Bay Bay 1061F East Bay (E) St. Andrew

Choctawhatchee - 3 3 16-0481 St. Andrews Bay Bay 1061F East Bay (East Segment) St. Andrew

Choctawhatchee - 1 3 05-1153 St. Andrews Bay Bay 1061FB Dupont Bridge St. Andrew

Choctawhatchee - North Bay (North 2 3 10-0539 St. Andrews Bay Bay 1061G St. Andrew Segment1)

Choctawhatchee - North Bay (North 3 3 16-0482 St. Andrews Bay Bay 1061G St. Andrew Segment1) Choctawhatchee - North Bay (North 3 3 16-0483 St. Andrews Bay Bay 1061H St. Andrew Segment2)

Choctawhatchee - North Bay (North 3 3 16-0484 St. Andrews Bay Bay 1061H St. Andrew Segment2)

Choctawhatchee - 3 3 16-0485 St. Andrews Bay Bay 1086 Mill Bayou St. Andrew

Choctawhatchee - 2 3 10-0487 St. Andrews Bay Bay 1088 Beatty Bayou St. Andrew

Ochlockonee - St. Coastal Watershed 4 1 19-0512 Wakulla 1089 Marks and Apalachee Bay

Ochlockonee - St. Coastal Watershed 4 1 19-0513 Wakulla 1089 East River Marks and Apalachee Bay

Choctawhatchee - 2 3 10-0495 St. Andrews Bay Bay, Calhoun, Gulf 1111 Sandy Creek St. Andrew

Choctawhatchee - 2 3 10-0496 St. Andrews Bay Bay, Calhoun, Gulf 1111 Sandy Creek St. Andrew

Choctawhatchee - Sandy Creek (Shellfish 3 3 16-0486 St. Andrews Bay Bay 1111A St. Andrew Portion)

Ochlockonee - St. 2 1 09-1996 Wakulla 1124 Big Boggy Branch Marks Choctawhatchee - 2 3 10-0504 St. Andrews Bay Bay 1128 Pretty Bayou St. Andrew

Choctawhatchee - 2 3 10-0506 St. Andrews Bay Bay 1131 Johnson Bayou St. Andrew

Choctawhatchee - 2 3 10-0508 St. Andrews Bay Bay 1136 Watson Bayou St. Andrew Choctawhatchee - 2 3 10-0543 St. Andrews Bay Bay 1141B Parker Bayou St. Andrew Choctawhatchee - 2 3 10-0510 St. Andrews Bay Bay 1142 Boggy Creek St. Andrew

Choctawhatchee - Boggy Creek (Shellfish 3 3 16-0487 St. Andrews Bay Bay 1142A St. Andrew Portion)

Choctawhatchee - 2 3 10-0511 St. Andrews Bay Bay 1144 Massalina Bayou St. Andrew

Choctawhatchee - 2 3 10-0513 St. Andrews Bay Bay, Gulf 1155 Little Sandy Creek St. Andrew

Choctawhatchee - 2 3 10-0515 St. Andrews Bay Bay 1162 Mule Creek St. Andrew Ochlockonee - St. Coastal Watershed 4 1 19-0514 Wakulla 1176B Purify Creek Marks and Apalachee Bay

Ochlockonee - St. Coastal Watershed 4 1 19-0515 Wakulla 1176C Oyster Bay Marks and Apalachee Bay

Choctawhatchee - 2 3 10-0522 St. Andrews Bay Bay 1209 Eagle Nest Bayou St. Andrew

Ochlockonee - St. Coastal Watershed Dickerson Bay (Shellfish 3 1 13-0072 Wakulla 1223 Marks and Apalachee Bay Portion)

Choctawhatchee - Choctawhatchee Jackson, 2 3 10-0466 123 Alligator Creek St. Andrew River Washington

Ochlockonee - St. Coastal Watershed 3 1 13-0073 Wakulla 1239 Direct Runoff to Bay Marks and Apalachee Bay

Ochlockonee - St. South Ochlockonee 3 1 13-0074 Franklin, Wakulla 1248A Ochlockonee Bay Marks River

Ochlockonee - St. South Ochlockonee 3 1 13-0075 Franklin, Wakulla 1248A Ochlockonee Bay Marks River

Apalachicola - 1 2 03-2389 New River Franklin 1256 Alligator Harbor Chipola Apalachicola - 1 2 03-2374 Apalachicola Bay Franklin 1266 St George Sound Chipola

Choctawhatchee - 3 3 16-0488 St. Andrews Bay Gulf 1267 St Joseph Bay St. Andrew

Choctawhatchee - 3 3 16-0489 St. Andrews Bay Gulf 1267 St Joseph Bay St. Andrew

Choctawhatchee - 3 3 16-0490 St. Andrews Bay Gulf 1267B Dixie Belle Beach St. Andrew

Choctawhatchee - St. Joe Bay Monument 1 3 05-1154 St. Andrews Bay Gulf 1267C St. Andrew Beach Apalachicola - 2 2 09-1686 New River Franklin 1268 Doyle Creek Chipola

Apalachicola - 2 2 09-1687 New River Franklin 1273 Cash Creek Chipola

Apalachicola - 1 2 03-2376 Apalachicola Bay Franklin 1274 Apalachicola Bay Chipola Apalachicola - 2 2 09-1618 Apalachicola Bay Franklin 1274 Apalachicola Bay Chipola

Apalachicola - 4 2 20-0241 Apalachicola Bay Franklin 1274 Apalachicola Bay Chipola

Apalachicola - 1 2 03-2378 Apalachicola Bay Franklin 1274A East Bay Chipola Apalachicola - 1 2 03-2377 Apalachicola Bay Franklin 1274A East Bay Chipola

Apalachicola - 4 2 20-0242 Apalachicola Bay Franklin 1274A East Bay Chipola

Apalachicola - 4 2 20-0243 Apalachicola Bay Gulf, Franklin 1274B1 St Vincent Sound Chipola

Apalachicola - 4 2 20-0244 Apalachicola Bay Franklin 1274B2 Big Bayou Chipola

Apalachicola - 2 2 09-1637 Apalachicola Bay Franklin 1274C Direct Runoff to Bay Chipola

Apalachicola - East River (Shellfish 4 2 20-0245 Franklin 1275B Chipola Portion)

Apalachicola - 2 2 09-1688 New River Franklin 1278 East Bayou Chipola

Apalachicola - 2 2 06-1690 New River Franklin 1279 West Bayou Chipola

Apalachicola - 2 2 09-1692 New River Franklin 1283 Blounts Bay Chipola Apalachicola - 2 2 09-1655 Apalachicola River Franklin 1286 Huckleberry Creek Chipola Apalachicola - 1 2 03-2380 Apalachicola Bay Gulf 1288 Money Bayou Chipola

Ochlockonee - St. South Ochlockonee Franklin, Liberty, 4 1 19-0516 1297A Marks River Wakulla

Ochlockonee - St. South Ochlockonee Leon, Liberty, 2 1 09-1979 1297B Ochlockonee River Marks River Wakulla

Ochlockonee - St. North Ochlockonee 4 1 19-0517 Gadsden, Leon 1297E Ochlockonee River Marks River

Ochlockonee - St. North Ochlockonee 4 1 19-0518 Gadsden, Leon 1297E Ochlockonee River Marks River

Ochlockonee - St. North Ochlockonee 4 1 19-0519 Gadsden, Leon 1297F Ochlockonee River Marks River

Ochlockonee - St. North Ochlockonee 4 1 19-0520 Gadsden, Leon 1297F Ochlockonee River Marks River

Ochlockonee - St. North Ochlockonee 4 1 19-0521 Gadsden, Leon 1297X (West) Marks River

Ochlockonee - St. North Ochlockonee 4 1 19-0522 Gadsden, Leon 1297X Lake Talquin (West) Marks River

Ochlockonee - St. North Ochlockonee 4 1 19-0523 Gadsden, Leon 1297X Lake Talquin (West) Marks River

Ochlockonee - St. North Ochlockonee 4 1 19-0524 Gadsden, Leon 1297Y Lake Talquin (Center) Marks River Ochlockonee - St. North Ochlockonee 4 1 19-0525 Gadsden, Leon 1297Y Lake Talquin (Center) Marks River

Ochlockonee - St. North Ochlockonee 4 1 19-0526 Gadsden, Leon 1297Y Lake Talquin (Center) Marks River

Ochlockonee - St. North Ochlockonee 4 1 19-0527 Gadsden, Leon 1297Z Lake Talquin (East) Marks River

Ochlockonee - St. North Ochlockonee 4 1 19-0528 Gadsden, Leon 1297Z Lake Talquin (East) Marks River

Ochlockonee - St. North Ochlockonee 4 1 19-0529 Gadsden, Leon 1297Z Lake Talquin (East) Marks River

Ochlockonee - St. North Ochlockonee 2 1 09-1316 Gadsden 1303 Quincy Creek Marks River

Ochlockonee - St. North Ochlockonee Quincy Creek (Potable 4 1 19-0530 Gadsden 1303 Marks River Portion)

Ochlockonee - St. North Ochlockonee 4 1 19-0531 Gadsden 1303A Quincy Creek Marks River Ochlockonee - St. North Ochlockonee 4 1 19-0532 Gadsden 1303A Quincy Creek Marks River

Ochlockonee - St. North Ochlockonee 4 1 19-0533 Gadsden 1303A Quincy Creek Marks River

2 1 09-1905 Suwannee Levy 1326 Sheephead Creek

3 1 13-0108 Suwannee Waccasassa River Levy 1328 Direct Runoff to Gulf

Lower 2 4 10-3229 Withlacoochee Citrus 1329A Cross Barge Canal Withlacoochee

Lower 3 4 17-0437 Withlacoochee Citrus 1329A Cross Florida Barge Canal Withlacoochee

Lower 3 4 17-0438 Withlacoochee Citrus, Sumter 1329D Withlacoochee River Withlacoochee

Lower 2 4 10-3234 Withlacoochee Marion 1329R Wilson Head Spring Withlacoochee

Lower 3 4 17-0439 Withlacoochee Marion 1329R Wilson Head Spring Withlacoochee

Lower Blue Spring (Citrus 2 4 12-0600 Withlacoochee Citrus 1329S Withlacoochee County) Lower Blue Spring (Citrus 3 4 17-0440 Withlacoochee Citrus 1329S Withlacoochee County)

Upper 3 4 17-0441 Withlacoochee Hernando 1329T Blue Sink (Blue Sink Lake) Withlacoochee

Upper 3 4 17-0442 Withlacoochee Hernando 1329T Blue Sink (Blue Sink Lake) Withlacoochee

Upper 3 4 17-0443 Withlacoochee Hernando 1329W Bystre Lake Withlacoochee

3 1 13-0109 Suwannee Waccasassa River Levy 1332 Direct Runoff to Gulf

3 1 13-0110 Suwannee Waccasassa River Levy 1333 Spring Run

4 1 19-0575 Suwannee Waccasassa River Levy 1333A Little King Spring

4 1 19-0576 Suwannee Waccasassa River Levy 1333B Big King Spring

2 1 09-1907 Suwannee Waccasassa River Levy 1335 Direct Runoff to Gulf

2 1 09-1908 Suwannee Waccasassa River Levy 1335 Direct Runoff to Gulf

3 1 13-0111 Suwannee Waccasassa River Levy 1335 Direct Runoff to Gulf Lower 3 4 17-0444 Withlacoochee Citrus, Levy 1337A Bypass Channel Withlacoochee

Lower 3 4 17-0445 Withlacoochee Citrus, Levy 1337A Bypass Channel Withlacoochee

Lower Gum Springs (Alligator 2 4 10-3237 Withlacoochee Marion, Sumter 1338A Withlacoochee Springs)

Lower Gum Springs (Alligator 3 4 17-0446 Withlacoochee Marion, Sumter 1338A Withlacoochee Springs)

Crystal River / Kings 2 5 13-1346 Springs Coast Citrus 1339 Cedar - Salt Creek Bay Planning Unit

Crystal River / Kings 3 5 18-0297 Springs Coast Citrus 1341I Crystal River Bay Planning Unit

Crystal River / Kings 3 5 18-0298 Springs Coast Citrus 1341I Crystal River Bay Planning Unit

Crystal River / Kings 3 5 18-0299 Springs Coast Citrus 1341I Crystal River Bay Planning Unit

Homosassa River 2 5 13-1347 Springs Coast Citrus 1345A Crystal River Bay Planning Unit

2 4 10-3227 Withlacoochee Lake Panasoffkee Sumter 1351B2 Canal 485A Springs Group 3 4 17-0447 Withlacoochee Lake Panasoffkee Sumter 1351B2 Canal 485A Springs Group

3 4 17-0448 Withlacoochee Lake Panasoffkee Sumter 1356A Fenney Spring

4 1 19-0575 Ocklawaha Unit Lake 1362 Bugg Spring Run

Upper 3 4 17-0449 Withlacoochee Sumter 1378 Big Gant Canal Withlacoochee

3 5 18-0300 Springs Coast Middle Coastal Hernando, Pasco 1392B Lake Hancock

3 5 18-0301 Springs Coast Middle Coastal Hernando, Pasco 1392B Lake Hancock

3 5 18-0302 Springs Coast Middle Coastal Hernando, Pasco 1392B Lake Hancock

3 5 18-0303 Springs Coast Middle Coastal Hernando, Pasco 1392B Lake Hancock

2 1 09-2046 Ocklawaha Palatlakaha River Lake, Polk 1406 Big Creek Reach 3 5 18-0304 Springs Coast Middle Coastal Pasco 1409A Moon Lake

3 5 18-0305 Springs Coast Middle Coastal Pasco 1409A Moon Lake

3 5 18-0306 Springs Coast Middle Coastal Pasco 1409A Moon Lake

Upper Kissimmee 1 4 06-0525 Osceola, Polk 1436 Horseshoe Creek Planning Unit

2 5 12-0563 Springs Coast Middle Coastal Pasco 1439 Salt Spring Run

Anclote River / Bayou 3 5 18-0307 Springs Coast Coastal Pinellas Pinellas 1440A Complex (Spring Bayou) County

Tampa Bay 4 2 20-0388 Hillsborough River Hillsborough 1443E Hillsborough River Tributaries

Tampa Bay Hillsborough River (below 4 2 20-0389 Hillsborough River Hillsborough 1443F Tributaries Reservoir)

Tampa Bay Hillsborough River (above 4 2 20-0390 Hillsborough River Hillsborough 1443I Tributaries Reservoir)

Sarasota Bay - 3 3 16-0552 Upper Polk 1449A Lake Deeson Peace - Myakka Sarasota Bay - 3 3 16-0553 Upper Peace River Polk 1449A Lake Deeson Peace - Myakka

Sarasota Bay - 3 3 16-0554 Upper Peace River Polk 1449A Lake Deeson Peace - Myakka

Tampa Bay 3 2 15-0827 Hillsborough River Hillsborough 1451 Lake Hanna Outlet Tributaries

Tampa Bay 3 2 15-0830 Hillsborough River Polk 1454 Fox Branch Tributaries

Tampa Bay 4 2 20-0391 Hillsborough River Hillsborough,Pasco 1455 Trout Creek Tributaries

Tampa Bay 3 2 15-0831 Hillsborough River Pasco 1462A Crystal Springs Tributaries

Tampa Bay Hillsborough River below 3 2 15-0832 Hillsborough River Pasco 1462D Tributaries Southside Branch

Coastal Old Tampa 2 1 09-2456 Tampa Bay Hillsborough 1463M Little Lake Wilson Bay Tributary

Coastal Old Tampa 4 1 19-0608 Tampa Bay Hillsborough 1463M Little Lake Wilson Bay Tributary

Coastal Old Tampa 3 1 13-0171 Tampa Bay Pasco 1464A Black Lake Bay Tributary

Coastal Old Tampa 4 1 19-0609 Tampa Bay Pasco 1464A Black Lake Bay Tributary Coastal Old Tampa 4 1 19-0610 Tampa Bay Hillsborough, Pasco 1464V Lake Hiawatha Bay Tributary

Coastal Old Tampa 4 1 19-0611 Tampa Bay Hillsborough, Pasco 1464V Lake Hiawatha Bay Tributary

Coastal Old Tampa 4 1 19-0612 Tampa Bay Hillsborough, Pasco 1464V Lake Hiawatha Bay Tributary

Coastal Old Tampa 4 1 19-0613 Tampa Bay Pasco 1464W Lake Ann (Parker) Bay Tributary

Coastal Old Tampa 4 1 19-0614 Tampa Bay Pasco 1464W Lake Ann (Parker) Bay Tributary

Coastal Old Tampa 4 1 19-0615 Tampa Bay Pasco 1464W Lake Ann (Parker) Bay Tributary

Coastal Old Tampa 4 1 19-0616 Tampa Bay Pasco 1464W Lake Ann (Parker) Bay Tributary Upper 3 4 17-0450 Withlacoochee Polk 1466 Lake Agnes Withlacoochee

Upper 3 4 17-0451 Withlacoochee Polk 1466 Lake Agnes Withlacoochee

Upper 3 4 17-0452 Withlacoochee Polk 1466 Lake Agnes Withlacoochee

Upper 3 4 17-0453 Withlacoochee Polk 1466 Lake Agnes Withlacoochee

Upper Kissimmee 3 4 17-0302 Kissimmee River Polk 1472 Lake Hatchineha Drain Planning Unit

Upper Kissimmee 2 4 10-3137 Kissimmee River Osceola, Polk 1472C Dead River Planning Unit

Coastal Old Tampa 4 1 19-0617 Tampa Bay Hillsborough 1473W Lake Juanita Bay Tributary

Coastal Old Tampa 4 1 19-0618 Tampa Bay Hillsborough 1473W Lake Juanita Bay Tributary Coastal Old Tampa 4 1 19-0619 Tampa Bay Hillsborough 1473W Lake Juanita Bay Tributary

Coastal Old Tampa 4 1 19-0620 Tampa Bay Hillsborough 1474A Lake Wastena Bay Tributary

Coastal Old Tampa 4 1 19-0621 Tampa Bay Hillsborough 1474A Lake Wastena Bay Tributary

Coastal Old Tampa 4 1 19-0622 Tampa Bay Hillsborough 1474A Lake Wastena Bay Tributary

Coastal Old Tampa 4 1 19-0623 Tampa Bay Hillsborough 1474A Lake Wastena Bay Tributary

Coastal Old Tampa 4 1 19-0624 Tampa Bay Hillsborough 1474W Lake Dead Lady Bay Tributary

Upper Kissimmee 3 4 17-0303 Kissimmee River Polk 1480 Lake Marion Planning Unit Upper Kissimmee 3 4 17-0304 Kissimmee River Polk 1480 Lake Marion Planning Unit

Upper Kissimmee 3 4 17-0305 Kissimmee River Polk 1480 Lake Marion Planning Unit

Coastal Old Tampa 4 1 19-0625 Tampa Bay Pinellas 1486A Lake Tarpon Bay Tributary

Coastal Old Tampa 4 1 19-0626 Tampa Bay Pinellas 1486A Lake Tarpon Bay Tributary

Sarasota Bay - 3 3 16-0555 Upper Peace River Polk 1488B Lake Rochelle Peace - Myakka

Sarasota Bay - 3 3 16-0556 Upper Peace River Polk 1488B Lake Rochelle Peace - Myakka Sarasota Bay - 3 3 16-0557 Upper Peace River Polk 1488C Lake Haines Peace - Myakka

Sarasota Bay - 3 3 16-0558 Upper Peace River Polk 1488C Lake Haines Peace - Myakka

Sarasota Bay - 3 3 16-0559 Upper Peace River Polk 1488D Lake Alfred Peace - Myakka

Sarasota Bay - 3 3 16-0560 Upper Peace River Polk 1488D Lake Alfred Peace - Myakka

Sarasota Bay - 3 3 16-0561 Upper Peace River Polk 1488U Lake Conine Peace - Myakka

Sarasota Bay - 3 3 16-0562 Upper Peace River Polk 1488U Lake Conine Peace - Myakka

Sarasota Bay - 3 3 16-0563 Upper Peace River Polk 1488U Lake Conine Peace - Myakka Tampa Bay 3 2 15-0833 Hillsborough River Hillsborough 1489 Two Hole Branch Tributaries

2 5 12-0042 Perdido Escambia 149 McDavid Creek

Tampa Bay 3 2 15-0834 Hillsborough River Hillsborough, Polk 1490 Polk Creek Tributaries

Tampa Bay 4 2 20-0392 Hillsborough River Polk 1491B Galloway Lake Tributaries

Tampa Bay 4 2 20-0393 Hillsborough River Polk 1491B Galloway Lake Tributaries

Tampa Bay 4 2 20-0394 Hillsborough River Polk 1491B Galloway Lake Tributaries

Tampa Bay 4 2 20-0395 Hillsborough River Polk 1491B Galloway Lake Tributaries

Coastal Old Tampa 4 1 19-0627 Tampa Bay Hillsborough 1493D Williams Lake Bay Tributary

Coastal Old Tampa 4 1 19-0628 Tampa Bay Hillsborough 1493D Williams Lake Bay Tributary

Tampa Bay 2 2 09-2312 Hillsborough River Hillsborough 1495A Itchepackasassa Creek Tributaries Tampa Bay 1 2 03-2280 Hillsborough River Hillsborough, Polk 1495B Itchepackesassa Creek Tributaries Sarasota Bay - 2 3 10-0229 Upper Peace River Polk 1497 Saddle Creek Peace - Myakka

Sarasota Bay - 3 3 16-0564 Upper Peace River Polk 1497 Saddle Creek Peace - Myakka

Sarasota Bay - 3 3 16-0568 Upper Peace River Polk 1497B Lake Parker Peace - Myakka

Sarasota Bay - 3 3 16-0569 Upper Peace River Polk 1497B Lake Parker Peace - Myakka

Sarasota Bay - 3 3 16-0570 Upper Peace River Polk 1497B Lake Parker Peace - Myakka

Sarasota Bay - 3 3 16-0571 Upper Peace River Polk 1497B Lake Parker Peace - Myakka

Sarasota Bay - 3 3 16-0572 Upper Peace River Polk 1497D1 Lake Crago Peace - Myakka

Sarasota Bay - 3 3 16-0573 Upper Peace River Polk 1497D1 Lake Crago Peace - Myakka

Sarasota Bay - 3 3 16-0574 Upper Peace River Polk 1497G Lake Mirror Peace - Myakka Sarasota Bay - 3 3 16-0575 Upper Peace River Polk 1497G Lake Mirror Peace - Myakka

Sarasota Bay - 3 3 16-0576 Upper Peace River Polk 1497H Lake Morton Peace - Myakka

Sarasota Bay - 3 3 16-0577 Upper Peace River Polk 1497H Lake Morton Peace - Myakka

Sarasota Bay - 3 3 16-0578 Upper Peace River Polk 1497J Saddle Creek Lakes Peace - Myakka

Sarasota Bay - 3 3 16-0579 Upper Peace River Polk 1497J Saddle Creek Lakes Peace - Myakka

Sarasota Bay - 3 3 16-0580 Upper Peace River Polk 1497J Saddle Creek Lakes Peace - Myakka Coastal Old Tampa 4 1 19-0629 Tampa Bay Hillsborough 1498 Brushy Creek Bay Tributary

Tampa Bay 3 2 15-0835 Hillsborough River Hillsborough 1499 Thirteen Mile Creek Tributaries

Sarasota Bay - 3 3 16-0581 Upper Peace River Polk 15002 Middle Lake Hamilton Peace - Myakka

Sarasota Bay - 3 3 16-0582 Upper Peace River Polk 15002 Middle Lake Hamilton Peace - Myakka

Sarasota Bay - 3 3 16-0583 Upper Peace River Polk 15002 Middle Lake Hamilton Peace - Myakka

Sarasota Bay - 3 3 16-0584 Upper Peace River Polk 15002 Middle Lake Hamilton Peace - Myakka

Sarasota Bay - 2 3 10-0235 Upper Peace River Polk 1501A Lake Lena Run Peace - Myakka

Sarasota Bay - 3 3 16-0585 Upper Peace River Polk 1501B Lake Ariana Peace - Myakka Sarasota Bay - 3 3 16-0586 Upper Peace River Polk 1501B Lake Ariana Peace - Myakka

Sarasota Bay - 3 3 16-0587 Upper Peace River Polk 1501V Spirit Lake Peace - Myakka

Sarasota Bay - 3 3 16-0588 Upper Peace River Polk 1501W Sears Lake Peace - Myakka

Coastal Old Tampa 4 1 19-0630 Tampa Bay Hillsborough 1502C Chapman Lake Bay Tributary

Sarasota Bay - 3 3 16-0589 Upper Peace River Polk 15041 Lake Hamilton Peace - Myakka

Sarasota Bay - 3 3 16-0590 Upper Peace River Polk 15041 Lake Hamilton Peace - Myakka

Tampa Bay 3 2 15-0836 Hillsborough River Hillsborough 1505 Clay Gully Tributaries

Tampa Bay 3 2 15-0837 Hillsborough River Polk 1506A Meadow View Lake Tributaries Tampa Bay 3 2 15-0838 Hillsborough River Polk 1506A Meadow View Lake Tributaries

Coastal Old Tampa 2 1 09-2468 Tampa Bay Hillsborough 1507A Channel A Bay Tributary

Coastal Old Tampa 4 1 19-0631 Tampa Bay Hillsborough 1507A Rocky Creek (Channel A) Bay Tributary

Coastal Old Tampa 4 1 19-0632 Tampa Bay Hillsborough 1507A Rocky Creek (Channel A) Bay Tributary

Coastal Old Tampa 4 1 19-0633 Tampa Bay Hillsborough 1507A Rocky Creek (Channel A) Bay Tributary

Anclote River / Klosterman Bayou Run 1 5 09-1040 Springs Coast Coastal Pinellas Pinellas 1508 Tidal County

Anclote River / Klosterman Bayou Run 1 5 09-1041 Springs Coast Coastal Pinellas Pinellas 1508 Tidal County

Anclote River / 3 5 18-0308 Springs Coast Coastal Pinellas Pinellas 1508 Klosterman Bayou County

Anclote River / 2 5 12-0500 Springs Coast Coastal Pinellas Pinellas 1508A Klosterman Bayou Run County

Anclote River / 2 5 12-0501 Springs Coast Coastal Pinellas Pinellas 1508A Klosterman Bayou Run County

Anclote River / 2 5 12-0502 Springs Coast Coastal Pinellas Pinellas 1508A Klosterman Bayou Run County Anclote River / 3 5 18-0309 Springs Coast Coastal Pinellas Pinellas 1508A Klosterman Bayou Run County

Anclote River / 3 5 18-0310 Springs Coast Coastal Pinellas Pinellas 1508A Klosterman Bayou Run County

Sarasota Bay - 3 3 16-0591 Upper Peace River Polk 15101 Lake Eva Peace - Myakka

Sarasota Bay - 3 3 16-0592 Upper Peace River Polk 15101 Lake Eva Peace - Myakka

Anclote River / Wall Spring (Health 3 5 18-0311 Springs Coast Coastal Pinellas Pinellas 1512Z Springs) County

Coastal Old Tampa Hillsborough, Double Branch 4 1 19-0634 Tampa Bay 1513E Bay Tributary Pinellas (Freshwater Segment)

Coastal Old Tampa Double Branch (Estuarine 4 1 19-0635 Tampa Bay Hillsborough 1513F Bay Tributary Segment)

Coastal Old Tampa Rocky Creek (Upper-Mid 3 1 13-0178 Tampa Bay Hillsborough 1517 Bay Tributary Segment)

Tampa Bay 3 2 15-0839 Hillsborough River Hillsborough 1518 East Canal Tributaries

Tampa Bay 3 2 15-0840 Hillsborough River Hillsborough 1520 Hollomans Branch Tributaries Sarasota Bay - 3 3 16-0593 Upper Peace River Polk 1521B Lake Eloise Peace - Myakka

Sarasota Bay - 3 3 16-0594 Upper Peace River Polk 1521B Lake Eloise Peace - Myakka

Sarasota Bay - 2 3 10-0241 Upper Peace River Polk 1521C Lake Lulu Run Peace - Myakka

Sarasota Bay - 2 3 10-0242 Upper Peace River Polk 1521C Lake Lulu Run Peace - Myakka

Sarasota Bay - 2 3 10-0243 Upper Peace River Polk 1521C Lake Lulu Run Peace - Myakka

Sarasota Bay - 3 3 16-0595 Upper Peace River Polk 1521I Lake Hartridge Peace - Myakka

Sarasota Bay - 3 3 16-0596 Upper Peace River Polk 1521I Lake Hartridge Peace - Myakka

Sarasota Bay - 3 3 16-0597 Upper Peace River Polk 1521I Lake Hartridge Peace - Myakka

Sarasota Bay - 3 3 16-0598 Upper Peace River Polk 1521L Lake Marianna Peace - Myakka Sarasota Bay - 3 3 16-0599 Upper Peace River Polk 1521L Lake Marianna Peace - Myakka

Sarasota Bay - 3 3 16-0600 Upper Peace River Polk 1521P Deer Lake Peace - Myakka

Sarasota Bay - 3 3 16-0601 Upper Peace River Polk 1521Q Lake Blue Peace - Myakka

Sarasota Bay - 3 3 16-0602 Upper Peace River Polk 1521Q Lake Blue Peace - Myakka

Sarasota Bay - 3 3 16-0603 Upper Peace River Polk 1521Q Lake Blue Peace - Myakka

Tampa Bay 3 2 15-0841 Hillsborough River Hillsborough 1522B Lake Thonotosassa Tributaries

Tampa Bay 3 2 15-0845 Hillsborough River Hillsborough 1522C Baker Creek Tributaries

Tampa Bay 4 2 20-0396 Hillsborough River Hillsborough 1522E Baker Creek East Tributaries

Tampa Bay 3 2 15-0847 Hillsborough River Hillsborough 1523 Curiosity Creek Tributaries Anclote River / 2 5 12-0506 Springs Coast Coastal Pinellas Pinellas 1527B Bee Branch County

Anclote River / 3 5 18-0312 Springs Coast Coastal Pinellas Pinellas 1527B Bee Branch County

Anclote River / 3 5 18-0313 Springs Coast Coastal Pinellas Pinellas 1527B Bee Branch County

Anclote River / 3 5 18-0314 Springs Coast Coastal Pinellas Pinellas 1527B Bee Branch County

Anclote River / 3 5 18-0315 Springs Coast Coastal Pinellas Pinellas 1528A The Narrows County

Coastal Old Tampa 4 1 19-0636 Tampa Bay Pinellas 1529 Cow Branch Bay Tributary

Coastal Old Tampa 3 1 13-0181 Tampa Bay Pinellas 1529B South Creek Bay Tributary

Coastal Old Tampa 3 1 13-0182 Tampa Bay Pinellas 1529B South Creek Bay Tributary Coastal Old Tampa 1 1 02-1384 Tampa Bay Pinellas 1530 Moccasin Creek Bay Tributary

Coastal Old Tampa 2 1 09-2432 Tampa Bay Pinellas 1530 Moccasin Creek Tidal Bay Tributary

Coastal Old Tampa 2 1 09-2472 Tampa Bay Pinellas 1530A Moccasin Creek Bay Tributary

Coastal Old Tampa 4 1 19-0637 Tampa Bay Pinellas 1530A Moccasin Creek Bay Tributary

Coastal Old Tampa 4 1 19-0638 Tampa Bay Pinellas 1530A Moccasin Creek Bay Tributary

Coastal Old Tampa 4 1 19-0639 Tampa Bay Pinellas 1530A Moccasin Creek Bay Tributary

Upper Kissimmee 3 4 17-0306 Kissimmee River Polk 1532A Lake Pierce Planning Unit

Upper Kissimmee 3 4 17-0307 Kissimmee River Polk 1532A Lake Pierce Planning Unit

Upper Kissimmee 3 4 17-0308 Kissimmee River Polk 1532A Lake Pierce Planning Unit Tampa Bay 4 2 20-0397 Hillsborough River Hillsborough 1533 Campbell Branch Tributaries

Coastal Hillsborough 3 1 13-0183 Tampa Bay Hillsborough 1536A Unnamed Drain Bay Tributary

Coastal Hillsborough Sixmile Creek (Tampa 3 1 13-0184 Tampa Bay Hillsborough 1536B Bay Tributary Bypass Canal)

Coastal Hillsborough Sixmile Creek (Tampa 3 1 13-0185 Tampa Bay Hillsborough 1536B Bay Tributary Bypass Canal)

Coastal Hillsborough 3 1 13-0187 Tampa Bay Hillsborough 1536C Bay Tributary Tributary

Coastal Hillsborough 4 1 19-0640 Tampa Bay Hillsborough 1536E Palm River Bay Tributary

Coastal Hillsborough 2 1 09-2380 Tampa Bay Hillsborough 1536F Sixmile Creek Bay Tributary

Tampa Bay 2 2 09-2320 Hillsborough River Polk 1537 Lake Wire Tributaries

Tampa Bay 3 2 15-0849 Hillsborough River Polk 1537A Lake Bonnet Tributaries

Tampa Bay 3 2 15-0850 Hillsborough River Polk 1537A Lake Bonnet Tributaries Tampa Bay 4 2 20-0398 Hillsborough River Polk 1537A Lake Bonnet Tributaries

Tampa Bay 4 2 20-0399 Hillsborough River Polk 1537A Lake Bonnet Tributaries

Tampa Bay 4 2 20-0400 Hillsborough River Polk 1537A Lake Bonnet Tributaries

Anclote River / 1 5 09-1046 Springs Coast Coastal Pinellas Pinellas 1538 Curlew Creek Tidal County

Sarasota Bay - 3 3 16-0604 Upper Peace River Polk 1539C Lake Annie Peace - Myakka

Sarasota Bay - 3 3 16-0605 Upper Peace River Polk 1539D Lake Otis Peace - Myakka

Sarasota Bay - 3 3 16-0606 Upper Peace River Polk 1539D Lake Otis Peace - Myakka

Coastal Old Tampa 2 1 09-2475 Tampa Bay Pinellas 1541A Lake Tarpon Canal Bay Tributary Coastal Old Tampa 4 1 19-0641 Tampa Bay Pinellas 1541C Briar Creek Bay Tributary

Coastal Old Tampa 4 1 19-0642 Tampa Bay Pinellas 1541C Briar Creek Bay Tributary

Coastal Old Tampa 4 1 19-0643 Tampa Bay Pinellas 1541C Briar Creek Bay Tributary

Tampa Bay 4 2 20-0401 Hillsborough River Hillsborough 1542 Pemberton Creek Tributaries

Tampa Bay 4 2 20-0402 Hillsborough River Hillsborough 1542 Pemberton Creek Tributaries

Tampa Bay 3 2 15-0852 Hillsborough River Polk 1543A Lake Hunter Outlet Tributaries

Tampa Bay 4 2 20-0403 Hillsborough River Hillsborough 1547 Seffner Canal Tributaries

Tampa Bay 3 2 15-0854 Hillsborough River Hillsborough 1547A Lake Valrico Tributaries Tampa Bay 3 2 15-0855 Hillsborough River Hillsborough 1547A Lake Valrico Tributaries

Tampa Bay 3 2 15-0856 Hillsborough River Hillsborough 1547A Lake Valrico Tributaries

Tampa Bay 4 2 20-0404 Hillsborough River Hillsborough 1547A Lake Valrico Tributaries

Sarasota Bay - 1 3 05-1228 Upper Peace River Polk 1549A Banana Lake Canal Peace - Myakka

Sarasota Bay - 3 3 16-0607 Upper Peace River Polk 1549B Banana Lake Peace - Myakka

Sarasota Bay - 3 3 16-0608 Upper Peace River Polk 1549B Banana Lake Peace - Myakka

Sarasota Bay - 3 3 16-0609 Upper Peace River Polk 1549B Banana Lake Peace - Myakka Sarasota Bay - 3 3 16-0610 Upper Peace River Polk 1549B Banana Lake Peace - Myakka

Sarasota Bay - 3 3 16-0611 Upper Peace River Polk 1549B1 Lake Stahl Peace - Myakka

Sarasota Bay - 3 3 16-0612 Upper Peace River Polk 1549B1 Lake Stahl Peace - Myakka

Sarasota Bay - 3 3 16-0613 Upper Peace River Polk 1549B1 Lake Stahl Peace - Myakka

Sarasota Bay - 3 3 16-0614 Upper Peace River Polk 1549B1 Lake Stahl Peace - Myakka

Sarasota Bay - 3 3 16-0615 Upper Peace River Polk 1549B2 Little Banana Lake Peace - Myakka Sarasota Bay - 3 3 16-0616 Upper Peace River Polk 1549B2 Little Banana Lake Peace - Myakka

Sarasota Bay - 3 3 16-0617 Upper Peace River Polk 1549B2 Little Banana Lake Peace - Myakka

Sarasota Bay - 3 3 16-0618 Upper Peace River Polk 1549C Lake Bentley Peace - Myakka

Sarasota Bay - 3 3 16-0619 Upper Peace River Polk 1549D Lake Horney Peace - Myakka

Sarasota Bay - 3 3 16-0620 Upper Peace River Polk 1549E Lake John Peace - Myakka

Sarasota Bay - 3 3 16-0621 Upper Peace River Polk 1549E Lake John Peace - Myakka

Sarasota Bay - 3 3 16-0622 Upper Peace River Polk 1549E Lake John Peace - Myakka Sarasota Bay - 3 3 16-0623 Upper Peace River Polk 1549F Lake Somerset Peace - Myakka

Sarasota Bay - 3 3 16-0624 Upper Peace River Polk 1549F Lake Somerset Peace - Myakka

Sarasota Bay - 3 3 16-0625 Upper Peace River Polk 1549F Lake Somerset Peace - Myakka

Tampa Bay 3 2 15-0857 Hillsborough River Hillsborough 1553B Twin Lake Outlet Tributaries

Tampa Bay 3 2 15-0858 Hillsborough River Hillsborough 1555Z Tributaries

Anclote River / 1 5 09-1047 Springs Coast Coastal Pinellas Pinellas 1556 Cedar Creek Tidal County

Anclote River / 1 5 09-1048 Springs Coast Coastal Pinellas Pinellas 1556 Cedar Creek Tidal County

Hillsborough, 2 1 09-2493 Tampa Bay Lower Tampa Bay 1558A Tampa Bay Lower Manatee Hillsborough, 2 1 09-3494 Tampa Bay Middle Tampa Bay 1558BZ Tampa Bay Lower North Manatee, Pinellas

4 1 19-0644 Tampa Bay Middle Tampa Bay Hillsborough 1558CB E G Simmons Park 4 1 19-0645 Tampa Bay Middle Tampa Bay Hillsborough 1558CC Bahia Beach

4 1 19-0646 Tampa Bay Hillsborough Bay Hillsborough 1558EB Davis Island Beach

2 1 09-2500 Tampa Bay Old Tampa Bay Hillsborough 1558FB Picnic Island South

3 1 13-0188 Tampa Bay Old Tampa Bay Hillsborough 1558FC Picnic Island (North)

2 1 09-2504 Tampa Bay Old Tampa Bay Hillsborough 1558HB Ben T. Davis North

4 1 19-0647 Tampa Bay Old Tampa Bay Hillsborough 1558HC Ben T Davis (South)

4 1 19-0648 Tampa Bay Old Tampa Bay Hillsborough 1558HD Cypress Point Park (North)

Cypress Point Park 4 1 19-0649 Tampa Bay Old Tampa Bay Hillsborough 1558HE (South)

2 1 09-2509 Tampa Bay Old Tampa Bay Pinellas 1558IA Safety Harbor 3 1 13-0190 Tampa Bay Lower Tampa Bay Pinellas 1558N Boca Ciega Bay (South)

Coastal Old Tampa Rocky Creek (Lower 4 1 19-0650 Tampa Bay Hillsborough 1563 Bay Tributary Segment)

Tampa Bay 3 2 15-0859 Hillsborough River Hillsborough 1565 Moore Lake Drain Tributaries

Anclote River / Stevenson Creek (Tidal 2 5 12-0509 Springs Coast Coastal Pinellas Pinellas 1567 Segment) County

Anclote River / 1 5 09-1053 Springs Coast Coastal Pinellas Pinellas 1567B Spring Branch County Anclote River / 1 5 09-1052 Springs Coast Coastal Pinellas Pinellas 1567B Spring Branch County

Anclote River / 3 5 18-0316 Springs Coast Coastal Pinellas Pinellas 1567B Spring Branch County

Anclote River / 3 5 18-0317 Springs Coast Coastal Pinellas Pinellas 1567B Spring Branch County

Anclote River / 1 5 09-1055 Springs Coast Coastal Pinellas Pinellas 1567C Stevenson Creek County

Anclote River / Stevenson Creek (Fresh 3 5 18-0318 Springs Coast Coastal Pinellas Pinellas 1567C Segment) County Tampa Bay 4 2 20-0405 Hillsborough 1568 Howell Branch Tributaries

Coastal Old Tampa 4 1 19-0651 Tampa Bay Pinellas 1569 Bishop Creek (Tidal) Bay Tributary

Coastal Old Tampa 4 1 19-0652 Tampa Bay Pinellas 1569A Bishop Creek Bay Tributary

Coastal Old Tampa 4 1 19-0653 Tampa Bay Pinellas 1569A Bishop Creek Bay Tributary

Coastal Old Tampa 4 1 19-0654 Tampa Bay Pinellas 1569A Bishop Creek Bay Tributary

Coastal Old Tampa 4 1 19-0655 Tampa Bay Pinellas 1569A Bishop Creek Bay Tributary Coastal Old Tampa 4 1 19-0656 Tampa Bay Hillsborough 1570 Henry Street Canal Bay Tributary

Coastal Old Tampa Sweetwater Creek (Tidal 4 1 19-0657 Tampa Bay Hillsborough 1570A Bay Tributary Segment)

Upper Kissimmee 3 4 17-0309 Kissimmee River Polk 1573A Tiger Lake Planning Unit

Coastal Old Tampa 4 1 19-0658 Tampa Bay Pinellas 1574A Alligator Lake Bay Tributary

Coastal Old Tampa 4 1 19-0659 Tampa Bay Pinellas 1574A Alligator Lake Bay Tributary

Coastal Old Tampa 4 1 19-0660 Tampa Bay Pinellas 1575A Mullet Creek Bay Tributary

Coastal Old Tampa 4 1 19-0661 Tampa Bay Pinellas 1575A Mullet Creek Bay Tributary Coastal Old Tampa 4 1 19-0662 Tampa Bay Pinellas 1575A Mullet Creek Bay Tributary

Coastal Hillsborough 2 1 09-2361 Tampa Bay Hillsborough 1576 Mango Drain Bay Tributary

Coastal Hillsborough 3 1 13-0193 Tampa Bay Hillsborough 1576 Mango Drain Bay Tributary

Coastal Hillsborough 4 1 19-0663 Tampa Bay Hillsborough 1576A Mango Lake Bay Tributary

Coastal Hillsborough 4 1 19-0664 Tampa Bay Hillsborough 1576A Mango Lake Bay Tributary

Coastal Hillsborough 4 1 19-0665 Tampa Bay Hillsborough 1576A Mango Lake Bay Tributary

Coastal Old Tampa 4 1 19-0666 Tampa Bay Hillsborough 1577A Pepper Mound Creek Bay Tributary

Tampa Bay Turkey Creek above Little 4 2 20-0406 Alafia River Hillsborough 1578B Tributaries Alafia River Tampa Bay Turkey Creek above Little 4 2 20-0407 Alafia River Hillsborough 1578B Tributaries Alafia River

Tampa Bay Turkey Creek above Little 4 2 20-0408 Alafia River Hillsborough 1578B Tributaries Alafia River

Coastal Hillsborough 2 1 09-2364 Tampa Bay Hillsborough 1579 Bellows Lake Outlet Bay Tributary

Coastal Hillsborough 4 1 19-0667 Tampa Bay Hillsborough 1584A1 Drain Bay Tributary

Coastal Old Tampa 4 1 19-0668 Tampa Bay Hillsborough 1587A Woods Creek Bay Tributary

Sarasota Bay - 3 3 16-0626 Upper Peace River Polk 1588A Lake Mcleod Peace - Myakka

Tampa Bay Little Alafia River below 4 2 20-0409 Alafia River Hillsborough 1592 Tributaries Medard Reservoir

Tampa Bay Little Alafia River below 4 2 20-0410 Alafia River Hillsborough 1592 Tributaries Medard Reservoir Tampa Bay Little Alafia River below 4 2 20-0411 Alafia River Hillsborough 1592 Tributaries Medard Reservoir

Tampa Bay Little Alafia River above 4 2 20-0412 Alafia River Hillsborough 1592B Tributaries Medard Reservoir

Coastal Old Tampa 3 1 13-0202 Tampa Bay Hillsborough 1594 Fish Creek Bay Tributary

Coastal Old Tampa 4 1 19-0669 Tampa Bay Hillsborough 1594 Fish Creek Bay Tributary

Coastal Hillsborough 3 1 13-0203 Tampa Bay Hillsborough 1599 Uceta Yard Drain Bay Tributary

Coastal Old Tampa 4 1 19-0670 Tampa Bay Hillsborough 1601A Tampa Bay Channel Bay Tributary

Coastal Old Tampa 4 1 19-0671 Tampa Bay Pinellas 1603 Direct Runoff to Bay Bay Tributary

Coastal Old Tampa 1 1 02-1482 Tampa Bay Pinellas 1604 Allen Creek Bay Tributary

Coastal Old Tampa 4 1 19-0672 Tampa Bay Pinellas 1604 Allen Creek (Tidal) Bay Tributary

Coastal Old Tampa 4 1 19-0673 Tampa Bay Pinellas 1604 Allen Creek (Tidal) Bay Tributary

Coastal Old Tampa 4 1 19-0674 Tampa Bay Pinellas 1604B1 Allen Creek Bay Tributary Coastal Old Tampa 4 1 19-0675 Tampa Bay Pinellas 1604B1 Allen Creek Bay Tributary

Coastal Old Tampa 4 1 19-0676 Tampa Bay Pinellas 1604B1 Allen Creek Bay Tributary

Coastal Old Tampa 4 1 19-0677 Tampa Bay Pinellas 1604B1 Allen Creek Bay Tributary

Coastal Old Tampa 4 1 19-0678 Tampa Bay Pinellas 1604B2 Allen Creek Canal Bay Tributary

Coastal Hillsborough 4 1 19-0679 Tampa Bay Hillsborough 1605 Delaney Creek Bay Tributary

Coastal Hillsborough 2 1 09-2389 Tampa Bay Hillsborough 1605D Delaney Creek Tidal Bay Tributary

Coastal Hillsborough 3 1 13-0207 Tampa Bay Hillsborough 1605D Delaney Creek (Tidal) Bay Tributary

Coastal Hillsborough 3 1 13-0208 Tampa Bay Hillsborough 1605D Delaney Creek (Tidal) Bay Tributary Coastal Hillsborough 4 1 19-0680 Tampa Bay Hillsborough 1605D Delaney Creek (Tidal) Bay Tributary

3 4 17-0418 Pensacola Yellow River Okaloosa 160A Shoal River

1 4 06-0620 Pensacola Yellow River Okaloosa 160B Shoal River

Tampa Bay 2 2 09-2282 Alafia River Polk 1610 Mined Area Tributaries

Tampa Bay 3 2 15-0863 Alafia River Polk 1610 Carter Road Park Lakes Tributaries

Tampa Bay 3 2 15-0864 Alafia River Polk 1610 Carter Road Park Lakes Tributaries

Sarasota Bay - 3 3 16-0627 Upper Peace River Polk 1613A Lake Blue (South) Peace - Myakka

Anclote River / 1 5 09-1056 Springs Coast Coastal Pinellas Pinellas 1614 Belleair Golf Club Run County

Coastal Hillsborough 4 1 19-0681 Tampa Bay Hillsborough 1615 Drainage to McKay Bay Bay Tributary

Sarasota Bay - 3 3 16-0628 Upper Peace River Polk 1617A Lake Effie Peace - Myakka Sarasota Bay - 3 3 16-0629 Upper Peace River Polk 1617A Lake Effie Peace - Myakka

Sarasota Bay - 3 3 16-0630 Upper Peace River Polk 1617A Lake Effie Peace - Myakka

Anclote River / 2 5 12-0510 Springs Coast Coastal Pinellas Pinellas 1618C Long Bayou/Cross Bayou County Anclote River / 2 5 12-0511 Springs Coast Coastal Pinellas Pinellas 1618D Starkey Basin County

Lake Istokpoga 3 4 17-0310 Kissimmee River Polk 1619A Lake Wales Planning Unit

Lake Istokpoga 3 4 17-0311 Kissimmee River Polk 1619A Lake Wales Planning Unit

Lake Istokpoga 3 4 17-0312 Kissimmee River Polk 1619D Lake Moody Planning Unit

Tampa Bay 3 2 15-0867 Alafia River Hillsborough 1621F Lithia Springs Tributaries

Tampa Bay Alafia River above 4 2 20-0413 Alafia River Hillsborough 1621G Tributaries Hillsborough Bay

Sarasota Bay - Peace River Above 2 3 10-0151 Middle Peace River DeSoto 1623C Peace - Myakka Joshua Creek Sarasota Bay - Peace River above Oak 3 3 16-0631 Middle Peace River Hardee 1623E Peace - Myakka Creek

Sarasota Bay - Peace River above 3 3 16-0632 Upper Peace River Polk 1623J Peace - Myakka Bowlegs Creek

Sarasota Bay - Peace River above 3 3 16-0633 Upper Peace River Polk 1623J Peace - Myakka Bowlegs Creek

Sarasota Bay - Saddle Creek Below Lake 1 3 05-1243 Upper Peace River Polk 1623K Peace - Myakka Hancock

Sarasota Bay - Saddle Creek Below Lake 1 3 05-1244 Upper Peace River Polk 1623K Peace - Myakka Hancock

Sarasota Bay - Saddle Creek Below Lake 2 3 10-0268 Upper Peace River Polk 1623K Peace - Myakka Hancock

Sarasota Bay - Saddle Creek below Lake 3 3 16-0634 Upper Peace River Polk 1623K Peace - Myakka Hancock

Sarasota Bay - Saddle Creek below Lake 3 3 16-0635 Upper Peace River Polk 1623K Peace - Myakka Hancock

Sarasota Bay - 3 3 16-0636 Upper Peace River Polk 1623L Lake Hancock Peace - Myakka

Sarasota Bay - 3 3 16-0637 Upper Peace River Polk 1623L Lake Hancock Peace - Myakka Sarasota Bay - 3 3 16-0638 Upper Peace River Polk 1623L Lake Hancock Peace - Myakka

Sarasota Bay - 3 3 16-0639 Upper Peace River Polk 1623M Eagle Lake Peace - Myakka

Sarasota Bay - 3 3 16-0640 Upper Peace River Polk 1623M Eagle Lake Peace - Myakka

Sarasota Bay - 3 3 16-0641 Upper Peace River Polk 1623M Eagle Lake Peace - Myakka

Sarasota Bay - 3 3 16-0642 Upper Peace River Polk 1623T Engle Lake Peace - Myakka

Sarasota Bay - 3 3 16-0643 Upper Peace River Polk 1623T Engle Lake Peace - Myakka

Sarasota Bay - 3 3 16-0644 Upper Peace River Polk 1623T Engle Lake Peace - Myakka Sarasota Bay - 3 3 16-0645 Upper Peace River Polk 1623X Reclaimed Mine Cut Lake Peace - Myakka

Sarasota Bay - 3 3 16-0646 Upper Peace River Polk 1623X Reclaimed Mine Cut Lake Peace - Myakka

Sarasota Bay - 3 3 16-0647 Upper Peace River Polk 1623Z Fort Meade Lakes Peace - Myakka

Sarasota Bay - 3 3 16-0648 Upper Peace River Polk 1623Z Fort Meade Lakes Peace - Myakka

Sarasota Bay - 3 3 16-0649 Upper Peace River Polk 1623Z Fort Meade Lakes Peace - Myakka

Coastal Old Tampa 4 1 19-0682 Tampa Bay Pinellas 1625 Cross Canal (North) Bay Tributary

Sarasota Bay - West Wales Drainage 2 3 10-0270 Upper Peace River Polk 1626 Peace - Myakka Canal

Sarasota Bay - West Wales Drainage 2 3 10-0271 Upper Peace River Polk 1626 Peace - Myakka Canal

Coastal Old Tampa 4 1 19-0683 Tampa Bay Pinellas 1627B Long Branch (Tidal) Bay Tributary Coastal Hillsborough 3 1 13-0211 Tampa Bay Hillsborough 1628 Archie Creek Bay Tributary

Coastal Hillsborough 4 1 19-0684 Tampa Bay Hillsborough 1628A Archie Creek (Tidal) Bay Tributary

Sarasota Bay - 3 3 16-0650 Upper Peace River Polk 1631 Bear Branch Peace - Myakka

Coastal Hillsborough Delaney Creek Popoff 4 1 19-0685 Tampa Bay Hillsborough 1632 Bay Tributary Canal

Anclote River / McKay Creek Freshwater 1 5 09-1068 Springs Coast Coastal Pinellas Pinellas 1633B Segment County

Tampa Bay 3 2 15-0868 Alafia River Hillsborough 1635A Buckhorn Spring Tributaries

Tampa Bay 4 2 20-0414 Alafia River Hillsborough 1635B Buckhorn Creek Tributaries

Coastal Hillsborough 4 1 19-0686 Tampa Bay Hillsborough 1636 Port Sutton Ditch Bay Tributary

Anclote River / 1 5 09-1070 Springs Coast Coastal Pinellas Pinellas 1641 Cross Canal (South) County

Anclote River / 1 5 09-1071 Springs Coast Coastal Pinellas Pinellas 1641 Cross Canal (South) County

Anclote River / 3 5 18-0319 Springs Coast Coastal Pinellas Pinellas 1641 Cross Canal (South) County

Tampa Bay 4 2 20-0415 Alafia River Hillsborough 1642 Sloman Branch Tributaries Anclote River / 1 5 09-1072 Springs Coast Coastal Pinellas Pinellas 1643 Church Creek County

Tampa Bay 4 2 20-0416 Alafia River Hillsborough 1649 McCullough Branch Tributaries

Tampa Bay 4 2 20-0417 Alafia River Hillsborough 1651 McDonald Branch Tributaries

Tampa Bay 3 2 15-0872 Alafia River Hillsborough 1652 West Branch Tributaries

Tampa Bay 4 2 20-0418 Alafia River Hillsborough 1657 Little Fishhawk Creek Tributaries

Tampa Bay 4 2 20-0419 Alafia River Hillsborough 1659 Rice Creek Tributaries

Tampa Bay 4 2 20-0420 Alafia River Hillsborough 1660 Bell Creek Tributaries

Coastal Middle 2 1 09-2414 Tampa Bay Tampa Bay Pinellas 1661D Tinney Creek Tributary

Tampa Bay 4 2 20-0421 Alafia River Hillsborough,Polk 1665A Mizelle Creek Tributaries

Coastal Hillsborough 4 1 19-0687 Tampa Bay Hillsborough 1666 Bullfrog Creek Bay Tributary Coastal Hillsborough Bullfrog Creek (Tidal 4 1 19-0688 Tampa Bay Hillsborough 1666A Bay Tributary Segment)

Tampa Bay 4 2 20-0422 Alafia River Hillsborough 1667 Moccasin Creek Tributaries

Anclote River / 1 5 09-1078 Springs Coast Coastal Pinellas Pinellas 1668B Pinellas Park Ditch No. 5 County

Anclote River / Pinellas Park Ditch No 5 3 5 18-0320 Springs Coast Coastal Pinellas Pinellas 1668B (Bonn Creek) County

Anclote River / 1 5 09-1081 Springs Coast Coastal Pinellas Pinellas 1668D Bonn Creek County

Anclote River / 1 5 09-1082 Springs Coast Coastal Pinellas Pinellas 1668E St Joe Creek Tidal County

Anclote River / 1 5 09-1083 Springs Coast Coastal Pinellas Pinellas 1668E St Joe Creek Tidal County

Tampa Bay 3 2 15-0879 Alafia River Hillsborough 1669 Bell Creek Reservoir Tributaries

Tampa Bay 4 2 20-0423 Alafia River Hillsborough 1674 Pelleham Branch Tributaries

Tampa Bay 4 2 20-0424 Alafia River Hillsborough 1675 Owens Branch Tributaries Coastal Hillsborough 3 1 13-0216 Tampa Bay Hillsborough 1676 The Kitchen Bay Tributary

Coastal Hillsborough 3 1 13-0218 Tampa Bay Hillsborough 1676 The Kitchen Bay Tributary

Coastal Hillsborough 4 1 19-0689 Tampa Bay Hillsborough 1676 The Kitchen Bay Tributary

Sarasota Bay - 3 3 16-0651 Upper Peace River Polk 1677C Lake Buffum Peace - Myakka

Sarasota Bay - 3 3 16-0652 Upper Peace River Polk 1677C Lake Buffum Peace - Myakka

Sarasota Bay - 3 3 16-0653 Upper Peace River Polk 1677C Lake Buffum Peace - Myakka

Sarasota Bay - 3 3 16-0654 Upper Peace River Polk 1677C Lake Buffum Peace - Myakka

Tampa Bay 3 2 15-0882 Alafia River Hillsborough 1678 Chito Branch Tributaries Coastal Hillsborough 3 1 13-0219 Tampa Bay Hillsborough 1682 Kitchen Branch Bay Tributary

Coastal Hillsborough 4 1 19-0690 Tampa Bay Hillsborough 1682 Kitchen Branch Bay Tributary

Coastal Middle 4 1 19-0691 Tampa Bay Tampa Bay Pinellas 1683 Smacks Bayou Tributary

Coastal Middle 4 1 19-0692 Tampa Bay Tampa Bay Pinellas 1683 Smacks Bayou Tributary

Coastal Middle 4 1 19-0693 Tampa Bay Tampa Bay Pinellas 1683 Smacks Bayou Tributary

Tampa Bay 4 2 20-0425 Alafia River Hillsborough 1684 Halls Branch Tributaries

Lake Istokpoga 3 4 17-0313 Kissimmee River Polk 1685D Reedy Lake Planning Unit

Lake Istokpoga 3 4 17-0314 Kissimmee River Polk 1685D Reedy Lake Planning Unit Lake Istokpoga 3 4 17-0315 Kissimmee River Polk 1685E Lake Ida Planning Unit

Coastal Hillsborough 3 1 13-0222 Tampa Bay Hillsborough 1686 Unnamed Creek Bay Tributary

Anclote River / 3 5 18-0321 Springs Coast Coastal Pinellas Pinellas 1694B Boca Ciega Bay (North) County

Coastal Middle 4 1 19-0694 Tampa Bay Tampa Bay Pinellas 1696 Booker Creek Tributary

Coastal Middle 4 1 19-0695 Tampa Bay Tampa Bay Pinellas 1700 Coffeepot Bayou Tributary

Coastal Middle 4 1 19-0696 Tampa Bay Tampa Bay Pinellas 1700 Coffeepot Bayou Tributary

Coastal Middle 4 1 19-0697 Tampa Bay Tampa Bay Pinellas 1700 Coffeepot Bayou Tributary

Coastal Middle 4 1 19-0698 Tampa Bay Tampa Bay Pinellas 1700A Tributary

Coastal Middle 4 1 19-0699 Tampa Bay Tampa Bay Pinellas 1700A Crescent Lake Tributary Coastal Middle 4 1 19-0700 Tampa Bay Tampa Bay Pinellas 1700A Crescent Lake Tributary

Anclote River / 1 5 09-1085 Springs Coast Coastal Pinellas Pinellas 1701 Bear Creek County

Anclote River / 3 5 18-0322 Springs Coast Coastal Pinellas Pinellas 1701 Bear Creek County

Lake Istokpoga 3 4 17-0316 Kissimmee River Polk 1706 Lake Clinch Planning Unit

Lake Istokpoga 3 4 17-0317 Kissimmee River Polk 1706 Lake Clinch Planning Unit

Lake Istokpoga 3 4 17-0318 Kissimmee River Polk 1706 Lake Clinch Planning Unit

Coastal Middle 4 1 19-0701 Tampa Bay Tampa Bay Hillsborough 1708 Newman Branch Tributary

Coastal Middle 2 1 09-2415 Tampa Bay Tampa Bay Pinellas 1709D Little Bayou - Basin Q Tributary

Coastal Middle 2 1 09-2417 Tampa Bay Tampa Bay Pinellas 1709D Little Bayou - Basin Q Tributary Coastal Middle 4 1 19-0702 Tampa Bay Tampa Bay Pinellas 1709D Little Bayou - Basin Q Tributary

Coastal Middle 4 1 19-0703 Tampa Bay Tampa Bay Pinellas 1709D Little Bayou - Basin Q Tributary

Tampa Bay 3 2 15-0884 Alafia River Hillsborough 1711 Hurrah Creek Tributaries

Anclote River / Clam Bayou (East 3 5 18-0323 Springs Coast Coastal Pinellas Pinellas 1716C1 Drainage-North) County

Coastal Middle 4 1 19-0704 Tampa Bay Tampa Bay Hillsborough 1719 Symphony Isles Tributary

Tampa Bay 4 2 20-0426 Little Hillsborough 1724 Carlton Branch Tributaries

Coastal Middle 4 1 19-0705 Tampa Bay Tampa Bay Hillsborough 1725 Wolf Branch Cutoff Canal Tributary

Lake Istokpoga 3 4 17-0319 Kissimmee River Polk 1730 Hickory Lake Planning Unit

Lake Istokpoga 3 4 17-0320 Kissimmee River Polk 1730 Hickory Lake Planning Unit Lake Istokpoga 3 4 17-0321 Kissimmee River Polk 1730B Livingston Lake Planning Unit

Lake Istokpoga 3 4 17-0322 Kissimmee River Highlands 1730D Lake Adelaide Planning Unit

Lake Istokpoga 3 4 17-0323 Kissimmee River Highlands 1730D Lake Adelaide Planning Unit

Coastal Middle 3 1 13-0230 Tampa Bay Tampa Bay Pinellas 1731B Salt Creek Tributary

Tampa Bay 4 2 20-0427 Hillsborough 1732 Pierce Branch Tributaries

Coastal Middle 3 1 13-0231 Tampa Bay Tampa Bay Hillsborough 1736 Wolf Branch Tributary

Tampa Bay 3 2 15-0887 Little Manatee River Hillsborough 1739 Cypress Creek Tributaries

Tampa Bay Hillsborough,Manate 4 2 20-0428 Little Manatee River 1742A1 Little Manatee River Tributaries e

Tampa Bay Little Manatee River (North 4 2 20-0429 Little Manatee River Hillsborough 1742B Tributaries Fork)

Tampa Bay Little Manatee River 4 2 20-0430 Little Manatee River Hillsborough 1742C1 Tributaries (Tidal)

Tampa Bay 3 2 15-0889 Little Manatee River Hillsborough 1747A Ruskin Inlet Tributaries

Tampa Bay 3 2 15-0890 Little Manatee River Hillsborough 1747B Marsh Branch Tributaries Tampa Bay 4 2 20-0431 Little Manatee River Hillsborough 1749 Dug Creek Tributaries

Tampa Bay 3 2 15-0892 Little Manatee River Hillsborough 1754 Lake Wimauma Drain Tributaries

Tampa Bay 3 2 15-0893 Little Manatee River Hillsborough 1755 Gully Branch Tributaries

1 4 06-0583 Pensacola Blackwater River Santa Rosa 176 Pond Creek

Lake Istokpoga Arbuckle Creek above 3 4 17-0324 Kissimmee River Highlands 1761A Planning Unit Wildcat Slough

Lake Istokpoga Arbuckle Creek above 3 4 17-0325 Kissimmee River Highlands, Polk 1761B Planning Unit Morgan Hole Creek

Lake Istokpoga 2 4 10-3149 Kissimmee River Highlands, Polk 1761D1 Morgan Hole Creek Planning Unit

Tampa Bay 3 2 15-0894 Little Manatee River Hillsborough 1762A Howard Prairie Branch Tributaries

Sarasota Bay - Charlie Creek Above 2 3 10-0157 Middle Peace River Hardee 1763A Peace - Myakka Peace River

Sarasota Bay - Charlie Creek above 3 3 16-0656 Middle Peace River Hardee 1763A Peace - Myakka Peace River

Sarasota Bay - Charlie Creek above 3 3 16-0655 Middle Peace River Hardee 1763A Peace - Myakka Peace River Sarasota Bay - Charlie Creek above Old 3 3 16-0657 Middle Peace River Hardee, Polk 1763D Peace - Myakka Town Creek

Tampa Bay 3 2 15-0895 Little Manatee River Hillsborough 1768 Alderman Creek Tributaries

Tampa Bay Hillsborough, Tributay to Howard Prairie 3 2 15-0896 Little Manatee River 1770 Tributaries Manatee Branch

Tampa Bay 4 2 20-0432 Little Manatee River Hillsborough 1771 Heritage Park Creek Tributaries

Sarasota Bay - 2 3 10-0158 Middle Peace River Hardee, Polk 1774 Little Charlie Creek Peace - Myakka

Coastal Middle 4 1 19-0706 Tampa Bay Tampa Bay Hillsborough 1778 Cockroach Bay Tributary

Coastal Middle 4 1 19-0707 Tampa Bay Tampa Bay Hillsborough 1778 Cockroach Bay Tributary

Coastal Middle 4 1 19-0708 Tampa Bay Tampa Bay Hillsborough 1778 Cockroach Bay Tributary

Tampa Bay 4 2 20-0433 Little Manatee River Hillsborough 1780 Wildcat Creek Tributaries

Tampa Bay Hillsborough,Manate Carlton Branch (South 4 2 20-0434 Little Manatee River 1782 Tributaries e Segment)

Coastal Middle 3 1 13-0232 Tampa Bay Tampa Bay Hillsborough 1788 Cockroach Creek Tributary

Coastal Middle Hillsborough, 4 1 19-0709 Tampa Bay Tampa Bay 1789 Piney Point Creek Manatee Tributary Tampa Bay Hillsborough,Manate Little Manatee River 4 2 20-0435 Little Manatee River 1790 Tributaries e (South Fork)

Tampa Bay Hillsborough, 2 2 09-2341 Little Manatee River 1792 Unnamed Drainage Ditch Tributaries Manatee

Tampa Bay Hillsborough, 3 2 15-0900 Little Manatee River 1793 Unnamed Slough Tributaries Manatee

Coastal Lower 4 1 19-0710 Tampa Bay Tampa Bay Manatee 1797A Terra Ceia Bay Tributary

Coastal Lower 3 1 15-1543 Tampa Bay Tampa Bay Manatee 1797B Bishops Harbor Tributary

Tampa Bay Hillsborough, 3 2 15-0901 Little Manatee River 1798 Unnamed Branch Tributaries Manatee

Tampa Bay 2 2 09-2343 Little Manatee River Manatee 1800 Long Branch Tributaries

Tampa Bay 1 2 03-2338 Manatee River Manatee 1807B Lake Manatee Reservoir Tributaries

Tampa Bay 3 2 15-0903 Manatee River Manatee 1810 Gamble Creek Sink Tributaries

Lake Istokpoga 3 4 17-0326 Kissimmee River Highlands 1813L Lake Glenada Planning Unit

Tampa Bay 1 2 03-2342 Manatee River Manatee 1819 Gamble Creek Tributaries Coastal Lower 2 1 09-2395 Tampa Bay Tampa Bay Manatee 1823 Buffalo Creek Tributary

Coastal Lower Frog Creek (Tidal 4 1 19-0711 Tampa Bay Tampa Bay Manatee 1825A Segment) Tributary

Coastal Lower Frog Creek (Freshwater 3 1 13-0235 Tampa Bay Tampa Bay Manatee 1825B Segment) Tributary Tampa Bay 4 2 20-0436 Manatee River Manatee 1840 Gilley Creek Tributaries

Sarasota Bay - 2 3 10-0159 Middle Peace River Hardee 1844 Thompson Branch Peace - Myakka

Tampa Bay Manatee River above 4 2 20-0437 Manatee River Manatee 1848B Tributaries

Tampa Bay Manatee River above 4 2 20-0438 Manatee River Manatee 1848B Tributaries Braden River

Tampa Bay Wares Creek (Estuarine 4 2 20-0439 Manatee River Manatee 1848D1 Tributaries Segment)

Tampa Bay Wares Creek (Estuarine 4 2 20-0440 Manatee River Manatee 1848D1 Tributaries Segment)

Tampa Bay Wares Creek (Estuarine 4 2 20-0441 Manatee River Manatee 1848D1 Tributaries Segment)

Tampa Bay Wares Creek (Freshwater 4 2 20-0442 Manatee River Manatee 1848D2 Tributaries Segment)

Tampa Bay Wares Creek (Freshwater 4 2 20-0443 Manatee River Manatee 1848D2 Tributaries Segment)

Lower Kissimmee Highlands, 2 4 10-3154 Kissimmee River 1856A Istokpoga Canal Planning Unit Okeechobee Lower Kissimmee Highlands, 3 4 17-0327 Kissimmee River 1856A Istokpoga Canal Planning Unit Okeechobee

Lake Istokpoga 3 4 17-0328 Kissimmee River Highlands 1856B Lake Istokpoga Planning Unit

Lake Istokpoga 3 4 17-0329 Kissimmee River Highlands 1856B Lake Istokpoga Planning Unit

Lake Istokpoga 3 4 17-0330 Kissimmee River Highlands 1856B Lake Istokpoga Planning Unit

Lake Istokpoga 3 4 17-0331 Kissimmee River Highlands 1856B Lake Istokpoga Planning Unit

Lake Istokpoga 1 4 06-0514 Kissimmee River Highlands 1860A Josephine Creek Planning Unit

Lake Istokpoga 3 4 17-0332 Kissimmee River Highlands 1860A Josephine Creek Planning Unit

Lake Istokpoga 2 4 10-3157 Kissimmee River Highlands 1860C Jackson Creek Planning Unit Lake Istokpoga 3 4 17-0333 Kissimmee River Highlands 1860C Jackson Creek Planning Unit

Sarasota Bay - 1 3 05-1176 Upper Manatee 1869B Myakka River (Upper) Peace - Myakka

Sarasota Bay - Myakka River (Upper 3 3 16-0658 Upper Myakka River Manatee 1869C Peace - Myakka Segment)

Sarasota Bay - 2 3 10-0160 Middle Peace River Hardee 1871 Alligator Branch Peace - Myakka

Tampa Bay Mill Creek (Estuarine 4 2 20-0444 Manatee River Manatee 1872A Tributaries Segment)

Tampa Bay Mill Creek (Freshwater 3 2 15-0908 Manatee River Manatee 1872B Tributaries Segment)

Sarasota Bay - 3 3 16-0659 Middle Peace River Hardee 1873 Oak Creek Peace - Myakka

Tampa Bay 3 2 15-0909 Manatee River Manatee 1874 Gates Creek Tributaries

Tampa Bay Braden River below Ward 4 2 20-0445 Manatee River Manatee 1876 Tributaries Lake

Sarasota Bay - 1 3 05-1177 Upper Myakka River Manatee, Sarasota 1877A Myakka River (Upper) Peace - Myakka

Sarasota Bay - 3 3 16-0660 Lower Myakka River Sarasota 1877C Myakka River (North Fork) Peace - Myakka

Sarasota Bay - 3 3 16-0661 Lower Myakka River Sarasota 1877C Myakka River (North Fork) Peace - Myakka

Sarasota Bay - 2 3 10-0165 Sarasota Bay Manatee 1883 Palma Sola Bay Peace - Myakka

Sarasota Bay - 1 3 05-1271 Sarasota Bay Manatee 1883B Palma Sola North Peace - Myakka

Sarasota Bay - 1 3 05-1272 Sarasota Bay Manatee 1883C Palma Sola South Peace - Myakka Sarasota Bay - 3 3 16-0662 Sarasota Bay Manatee 1885A West Cedar Hammock Peace - Myakka

Tampa Bay 4 2 20-0446 Manatee River Manatee 1887 Sugarhouse Creek Tributaries

Tampa Bay 2 2 09-2355 Manatee River Manatee 1890 Webb Branch Tributaries Sarasota Bay - 2 3 10-0216 Upper Myakka River Manatee 1894 Young Creek Peace - Myakka Sarasota Bay - 1 3 05-1273 Sarasota Bay Manatee 1896 Bowlees Creek Peace - Myakka

Sarasota Bay - 1 3 05-1275 Sarasota Bay Manatee 1896 Bowlees Creek Peace - Myakka

Lake Istokpoga 2 4 10-3158 Kissimmee River Highlands 1898A Lake Wolf Outlet Planning Unit

Tampa Bay 4 2 20-0447 Manatee River Manatee 1899 Gap Creek Tributaries

Tampa Bay 4 2 20-0448 Manatee River Manatee 1899 Gap Creek Tributaries

Tampa Bay 1 2 03-2352 Manatee River Manatee 1901 Williams Creek Tributaries Tampa Bay 1 2 03-2354 Manatee River Manatee 1912 Unnamed Drain Tributaries

Sarasota Bay - 2 3 10-0171 Sarasota Bay Manatee, Sarasota 1916 Longboat Key Peace - Myakka

Sarasota Bay - 3 3 16-0663 Sarasota Bay Manatee, Sarasota 1924 Cow Pen Slough Peace - Myakka

Sarasota Bay - 2 3 10-0218 Upper Myakka River Manatee, Sarasota 1927 Oglebay Creek Peace - Myakka

Sarasota Bay - 2 3 10-0219 Upper Myakka River Manatee, Sarasota 1927 Oglebay Creek Peace - Myakka Tampa Bay 1 2 03-2369 Manatee River Manatee, Sarasota 1930A Cooper Creek Tributaries Sarasota Bay - 3 3 16-0664 Upper Myakka River Hardee, Manatee 1933 Owen Creek Peace - Myakka

Sarasota Bay - 3 3 16-0665 Upper Myakka River Hardee, Manatee 1933 Owen Creek Peace - Myakka

Sarasota Bay - 2 3 10-0176 Sarasota Bay Sarasota 1936 Whitaker Bayou (Tidal) Peace - Myakka

Sarasota Bay - 2 3 10-0177 Sarasota Bay Sarasota 1936 Whitaker Bayou (Tidal) Peace - Myakka

Sarasota Bay - 2 3 10-0179 Sarasota Bay Sarasota 1936 Whitaker Bayou (Tidal) Peace - Myakka

Sarasota Bay - 3 3 16-0666 Sarasota Bay Manatee, Sarasota 1936A Walker Creek Peace - Myakka

Sarasota Bay - 1 3 05-1276 Sarasota Bay Sarasota 1937 Philippi Creek Peace - Myakka

Lake Placid 3 4 17-0334 Kissimmee River Highlands 1938C Lake Placid Planning Unit

Lake Placid 3 4 17-0335 Kissimmee River Highlands 1938E Persimmon Lake Planning Unit

Lake Placid 3 4 17-0336 Kissimmee River Highlands 1938E Persimmon Lake Planning Unit

Lake Placid 3 4 17-0337 Kissimmee River Highlands 1938F Red Water Lake Planning Unit

Lake Placid 3 4 17-0338 Kissimmee River Highlands 1938F Red Water Lake Planning Unit

Lake Placid 3 4 17-0339 Kissimmee River Highlands 1938F Red Water Lake Planning Unit Lake Placid 2 4 10-3160 Kissimmee River Highlands 1938Y Lake Placid Outlet Planning Unit

Lake Placid 2 4 10-3161 Kissimmee River Highlands 1938Y Lake Placid Outlet Planning Unit

Lake Placid 3 4 17-0340 Kissimmee River Highlands 1938Y Lake Placid Outlet Planning Unit

Sarasota Bay - 3 3 16-0667 Middle Peace River Desoto, Hardee 1939 Brandy Branch Peace - Myakka

Sarasota Bay - 3 3 16-0668 Upper Myakka River Sarasota 1940 Howard Creek Peace - Myakka

Sarasota Bay - 3 3 16-0669 Upper Myakka River Sarasota 1940 Howard Creek Peace - Myakka

Sarasota Bay - 3 3 16-0670 Upper Myakka River Sarasota 1943 Indian Creek Peace - Myakka

Sarasota Bay - 3 3 16-0671 Sarasota Bay Sarasota 1947 Philippi Creek (Tidal) Peace - Myakka

Sarasota Bay - 2 3 10-0182 Sarasota Bay Sarasota 1953 Hudson Bayou Tidal Peace - Myakka Sarasota Bay - 2 3 10-0183 Sarasota Bay Sarasota 1953 Hudson Bayou Tidal Peace - Myakka

Sarasota Bay - 3 3 16-0672 Sarasota Bay Sarasota 1953A Drain to Hudson Bayou Peace - Myakka

Sarasota Bay - 3 3 16-0673 Lower Myakka River Manatee 1955 Wildcat Slough Peace - Myakka

Sarasota Bay - 1 3 05-1181 Lower Myakka River Manatee, Sarasota 1958 Mud Lake Slough Peace - Myakka

Sarasota Bay - 3 3 16-0674 Sarasota Bay Sarasota 1966 Philippe Creek Tributary Peace - Myakka

Sarasota Bay - 2 3 10-0092 Lower Myakka River Manatee 1967 Bud Slough Peace - Myakka

Sarasota Bay - 2 3 10-0187 Sarasota Bay Manatee, Sarasota 1968B Sarasota Bay Peace - Myakka Sarasota Bay - 3 3 16-0675 Sarasota Bay Sarasota 1968F Blackburn Bay Peace - Myakka

Sarasota Bay - Myakka River at Clay 3 3 16-0676 Lower Myakka River Sarasota 1972A Peace - Myakka Gully West

Sarasota Bay - 3 3 16-0677 Sarasota Bay Sarasota 1975 Elligraw Bayou Peace - Myakka

Sarasota Bay - 3 3 16-0678 Sarasota Bay Sarasota 1975 Elligraw Bayou Peace - Myakka

Sarasota Bay - 2 3 10-0192 Sarasota Bay Sarasota 1975A Clowers Creek Estuary Peace - Myakka

Sarasota Bay - 3 3 16-0679 Sarasota Bay Sarasota 1975A Clowers Creek Estuary Peace - Myakka

Sarasota Bay - 3 3 16-0680 Sarasota Bay Sarasota 1975A Clowers Creek Estuary Peace - Myakka

Sarasota Bay - 3 3 16-0681 Sarasota Bay Sarasota 1975B Matheny Creek Peace - Myakka

Sarasota Bay - 3 3 16-0682 Lower Myakka River Manatee, Sarasota 1976 Big Slough Canal Peace - Myakka

Sarasota Bay - 1 3 05-1183 Lower Myakka River Sarasota 1981B Myakka River Peace - Myakka

Sarasota Bay - 3 3 16-0683 Lower Myakka River Sarasota 1981B Myakka River Peace - Myakka

Sarasota Bay - Lake Myakka (Upper 3 3 16-0684 Lower Myakka River Sarasota 1981C Peace - Myakka Segment)

Sarasota Bay - 3 3 16-0685 Sarasota Bay Sarasota 1982 South Creek Peace - Myakka 1 2 03-2391 Charlotte Harbor Lemon Bay Charlotte, Sarasota 1983A Lemon Bay

3 2 15-0705 Charlotte Harbor Lemon Bay Charlotte, Sarasota 1983A Upper Lemon Bay

3 2 15-0706 Charlotte Harbor Lemon Bay Charlotte, Sarasota 1983A Upper Lemon Bay

4 2 20-0258 Charlotte Harbor Lemon Bay Charlotte,Sarasota 1983A Upper Lemon Bay

2 2 09-1749 Charlotte Harbor Lemon Bay Sarasota 1983A1 North Lemon Bay

Lemon Bay (North 3 2 15-0707 Charlotte Harbor Lemon Bay Sarasota 1983A1 Segment)

1 2 03-2392 Charlotte Harbor Lemon Bay Charlotte 1983B Lemon Bay

Sarasota Bay - 3 3 16-0686 Sarasota Bay Sarasota 1984 Catfish Creek (Tidal) Peace - Myakka

Sarasota Bay - 2 3 10-0201 Sarasota Bay Sarasota 1984A North Creek (Tidal) Peace - Myakka

Sarasota Bay - 2 3 10-0202 Sarasota Bay Sarasota 1984A North Creek (Tidal) Peace - Myakka

Sarasota Bay - 2 3 10-0204 Sarasota Bay Sarasota 1984A North Creek (Tidal) Peace - Myakka

Sarasota Bay - 3 3 16-0687 Sarasota Bay Sarasota 1984A North Creek (Tidal) Peace - Myakka Sarasota Bay - 3 3 16-0688 Sarasota Bay Sarasota 1984AA Catfish Creek Peace - Myakka

Sarasota Bay - 2 3 10-0099 Lower Myakka River Charlotte, Sarasota 1991A Myakka River Peace - Myakka

Sarasota Bay - 3 3 16-0689 Lower Myakka River Charlotte, Sarasota 1991A Myakka River Peace - Myakka

Sarasota Bay - 1 3 05-1187 Lower Myakka River Charlotte, Sarasota 1991B Myakka River Peace - Myakka

Sarasota Bay - 2 3 10-0101 Lower Myakka River Charlotte, Sarasota 1991B Myakka River Peace - Myakka

Sarasota Bay - 3 3 16-0690 Lower Myakka River Charlotte, Sarasota 1991B Myakka River Peace - Myakka

Sarasota Bay - 3 3 16-0691 Lower Myakka River Charlotte, Sarasota 1991B Myakka River Peace - Myakka

Sarasota Bay - 3 3 16-0692 Lower Myakka River Sarasota 1991C Myakka River Peace - Myakka

Sarasota Bay - 2 3 10-0119 Lower Peace River DeSoto 1995 Myrtle Slough Peace - Myakka Sarasota Bay - 2 3 10-0120 Lower Peace River DeSoto 1995 Myrtle Slough Peace - Myakka Sarasota Bay - 2 3 10-0121 Lower Peace River DeSoto 1995 Myrtle Slough Peace - Myakka

Sarasota Bay - 3 3 16-0693 Lower Peace River Desoto 1995 Myrtle Slough Peace - Myakka

Sarasota Bay - 2 3 10-0161 Middle Peace River DeSoto 1997 Hawthorne Creek Peace - Myakka

Sarasota Bay - 3 3 16-0694 Middle Peace River Desoto 1997 Hawthorne Creek Peace - Myakka Sarasota Bay - 3 3 16-0695 Middle Peace River Desoto 2001 Hog Bay Peace - Myakka

Sarasota Bay - 3 3 16-0696 Sarasota Bay Sarasota 2002 Dona Bay Peace - Myakka

Sarasota Bay - 3 3 16-0697 Sarasota Bay Sarasota 2002 Dona Bay Peace - Myakka

Sarasota Bay - 3 3 16-0698 Lower Peace River Desoto 2008 Thornton Branch Peace - Myakka

Sarasota Bay - 3 3 16-0699 Sarasota Bay Sarasota 2009B Curry Creek (Tidal Portion) Peace - Myakka

Sarasota Bay - Curry Creek (Freshwater 3 3 16-0700 Sarasota Bay Sarasota 2009C Peace - Myakka Portion)

Sarasota Bay - 3 3 16-0701 Sarasota Bay Sarasota 2015 Hatchett Creek (Tidal) Peace - Myakka

Sarasota Bay - 3 3 16-0702 Sarasota Bay Sarasota 2015A Hatchett Creek Peace - Myakka

Sarasota Bay - 3 3 16-0703 Sarasota Bay Sarasota 2018A Roberts Bay Peace - Myakka

Sarasota Bay - ICWW (Sarasota County 3 3 16-0704 Sarasota Bay Sarasota 2018B Peace - Myakka Near Venice)

Alligator Creek (Tidal 4 2 20-0259 Charlotte Harbor Lemon Bay Sarasota 2030 Segment) Sarasota Bay - 3 3 16-0705 Lower Peace River Desoto 2033 Bobcat Creek Peace - Myakka

Sarasota Bay - 2 3 10-0122 Lower Peace River Charlotte, DeSoto 2035 Lee Branch Peace - Myakka 2 2 09-1755 Charlotte Harbor Lemon Bay Sarasota 2039 Forked Creek

Sarasota Bay - 3 3 16-0706 Lower Peace River Charlotte 2040 Myrtle Slough Peace - Myakka

Sarasota Bay - 3 3 16-0708 Lower Peace River Charlotte 2040 Myrtle Slough Peace - Myakka

Sarasota Bay - 3 3 16-0707 Lower Peace River Charlotte 2040 Myrtle Slough Peace - Myakka

Sarasota Bay - 3 3 16-0709 Lower Peace River Charlotte 2041 Shell Creek Peace - Myakka

Sarasota Bay - 3 3 16-0710 Lower Peace River Charlotte 2041 Shell Creek Peace - Myakka

Sarasota Bay - Shell Creek below 3 3 16-0711 Lower Peace River Charlotte 2041A Peace - Myakka Hendrickson Dam

Sarasota Bay - Shell Creek below 3 3 16-0712 Lower Peace River Charlotte 2041A Peace - Myakka Hendrickson Dam

4 2 20-0260 Charlotte Harbor Lemon Bay Sarasota 2042 Woodmere Creek

Sarasota Bay - 2 3 10-0125 Lower Peace River Charlotte 2047 Manchester Way Peace - Myakka

Sarasota Bay - 2 3 10-0110 Lower Myakka River Charlotte 2048A Sam Knight Creek Peace - Myakka

Sarasota Bay - 2 3 10-0127 Lower Peace River Charlotte 2048B Huckaby Creek Peace - Myakka

Sarasota Bay - 2 3 10-0128 Lower Peace River Charlotte 2048C Flopbuck Creek Peace - Myakka Sarasota Bay - 3 3 16-0713 Lower Peace River Charlotte 2048C Flopbuck Creek Peace - Myakka

4 2 20-0261 Charlotte Harbor Lemon Bay Sarasota 2049 Gottfried Creek

Sarasota Bay - 3 3 16-0714 Lower Myakka River Charlotte 2053 Trailer Park Canal Peace - Myakka

Sarasota Bay - 3 3 16-0715 Lower Myakka River Charlotte 2053 Trailer Park Canal Peace - Myakka

Sarasota Bay - 2 3 10-0131 Lower Peace River Charlotte 2054 Myrtle Slough Peace - Myakka

Sarasota Bay - 2 3 10-0132 Lower Peace River Charlotte 2054 Myrtle Slough Peace - Myakka

Sarasota Bay - 1 3 05-1191 Lower Myakka River Charlotte 2055 Tippecanoe Bay Peace - Myakka

Sarasota Bay - 2 3 10-0114 Lower Myakka River Charlotte 2055 Tippecanoe Bay Peace - Myakka

Sarasota Bay - 3 3 16-0716 Lower Myakka River Charlotte 2055 Tippecanoe Bay Peace - Myakka

Sarasota Bay - Peace River Estuary 2 3 10-0134 Lower Peace River Charlotte 2056A Peace - Myakka (Lower Segment)

Sarasota Bay - Middle Peace River 2 3 10-0136 Lower Peace River Charlotte 2056B Peace - Myakka Estuary (Middle Segment)

Sarasota Bay - Middle Peace River 3 3 16-0717 Lower Peace River Charlotte 2056B Peace - Myakka Estuary (Middle Segment)

Peace River Sarasota Bay - 3 3 16-0718 Lower Peace River Charlotte 2056C2 Estuary(Upper Segment Peace - Myakka South) Peace River Sarasota Bay - 3 3 16-0719 Lower Peace River Charlotte 2056C2 Estuary(Upper Segment Peace - Myakka South)

Sarasota Bay - 2 3 10-0140 Lower Peace River Charlotte 2056D Alligator Bay Peace - Myakka

Sarasota Bay - 1 3 05-1266 Lower Peace River Charlotte 2059 Cleveland Cemetary Ditch Peace - Myakka

Sarasota Bay - Myakka Cutoff (Western 3 3 16-0720 Lower Peace River Charlotte 2060A1 Peace - Myakka Portion)

Sarasota Bay - Myakka Cutoff (Eastern 3 3 16-0721 Lower Peace River Charlotte 2060A2 Peace - Myakka Portion)

Sarasota Bay - 1 3 05-1268 Lower Peace River Charlotte 2061 Direct Runoff to Stream Peace - Myakka

Sarasota Bay - 2 3 10-0144 Lower Peace River Charlotte 2061 Direct Runoff to Stream Peace - Myakka

Charlotte Harbor 1 2 03-2395 Charlotte Harbor Charlotte 2065A Charlotte Harbor Upper Proper

Charlotte Harbor Charlotte Harbor (Upper 2 2 09-1740 Charlotte Harbor Charlotte 2065A Proper Segment)

Charlotte Harbor Charlotte Harbor (Upper 3 2 15-0708 Charlotte Harbor Charlotte 2065A Proper Segment)

Charlotte Harbor Charlotte Harbor (Upper 4 2 20-0262 Charlotte Harbor Charlotte 2065A Proper Segment)

Charlotte Harbor Charlotte Harbor (Upper 4 2 20-0263 Charlotte Harbor Charlotte 2065A Proper Segment)

Charlotte Harbor Charlotte Harbor (Middle 3 2 15-0709 Charlotte Harbor Charlotte 2065B Proper Segment1) Charlotte Harbor Charlotte Harbor (Middle 4 2 20-0264 Charlotte Harbor Charlotte 2065B Proper Segment1)

Charlotte Harbor 1 2 03-2398 Charlotte Harbor Charlotte 2065C Charlotte Harbor Mid Proper

Charlotte Harbor Charlotte Harbor (Lower 3 2 15-0711 Charlotte Harbor Lee 2065D Proper Segment1)

1 2 03-2399 Charlotte Harbor Pine Island Lee 2065E Pine Island Sound

Pine Island Sound (Upper 4 2 20-0265 Charlotte Harbor Pine Island Lee 2065E Segment)

1 2 04-2839 Charlotte Harbor Pine Island Lee 2065F Matalacha Pass

3 2 15-0712 Charlotte Harbor Pine Island Lee 2065F Matlacha Pass

Pine Island Sound (Lower 3 2 15-0713 Charlotte Harbor Pine Island Lee 2065G Segment)

Pine Island Sound (Lower 4 2 20-0266 Charlotte Harbor Pine Island Lee 2065G Segment) Pine Island Sound (Lower 4 2 20-0267 Charlotte Harbor Pine Island Lee 2065G Segment)

3 2 15-0714 Charlotte Harbor Pine Island Lee 2065H1 San Carlos Bay

4 2 20-0268 Charlotte Harbor Pine Island Lee 2065H1 San Carlos Bay

4 2 20-0269 Charlotte Harbor Pine Island Lee 2065H1 San Carlos Bay

Charlotte Harbor 3 2 15-0715 Charlotte Harbor Charlotte 2074 Alligator Creek Proper

Coral Creek (West 4 2 20-0270 Charlotte Harbor Lemon Bay Charlotte 2078A Branch)

Coral Creek (West 4 2 20-0271 Charlotte Harbor Lemon Bay Charlotte 2078A Branch)

Coral Creek (West 4 2 20-0272 Charlotte Harbor Lemon Bay Charlotte 2078A Branch)

Coral Creek (West 4 2 20-0273 Charlotte Harbor Lemon Bay Charlotte 2078A Branch)

Coral Creek (West 4 2 20-0274 Charlotte Harbor Lemon Bay Charlotte 2078A Branch) 1 2 03-3402 Charlotte Harbor Pine Island Lee 2092E Pine Island

4 2 20-0275 Charlotte Harbor Pine Island Lee 2092G Sanibel Bayous

The Dunes Community 4 2 20-0276 Charlotte Harbor Pine Island Lee 2092H Stormwater Lakes

The Dunes Community 4 2 20-0277 Charlotte Harbor Pine Island Lee 2092H Stormwater Lakes

The Dunes Community 4 2 20-0278 Charlotte Harbor Pine Island Lee 2092H Stormwater Lakes

The Dunes Community 4 2 20-0279 Charlotte Harbor Pine Island Lee 2092H Stormwater Lakes

Middle St. Marys 3 4 17-0413 Nassau - St. Marys Nassau 2097E St Marys River River Unit

Middle St. Marys 3 4 17-0414 Nassau - St. Marys Nassau 2097G St Marys River River Unit

Lower St. Marys 3 4 17-0415 Nassau - St. Marys Nassau 2097N St Marys River River Unit

2 4 10-3119 Nassau - St. Marys Nassau River Nassau 2120B Mills Creek

3 4 17-0416 Nassau - St. Marys Nassau River Duval, Nassau 2148B Nassau River 1 4 06-0563 Nassau - St. Marys Nassau River Nassau 2156 Unnamed Branch

1 2 03-2409 Lower St. Johns North Mainstem Unit Duval 2181 Dunn Creek

Dunn Creek (Marine 4 2 20-0280 Lower St. Johns North Mainstem Duval 2181A Segment)

3 2 15-0717 Lower St. Johns North Mainstem Unit Duval 2187 Beeghly Heights Drain

Rushing Branch 3 2 15-0718 Lower St. Johns North Mainstem Unit Duval 2189A (Freshwater Segment)

Broward River (Upstream 3 2 15-0719 Lower St. Johns North Mainstem Unit Duval 2191B Marine Segment)

Middle St. Marys 2 4 10-3118 Nassau - St. Marys Nassau 2196 Deep Creek River

3 2 15-0720 Lower St. Johns Duval 2203A Trout River (Lower Reach)

4 2 20-0281 Lower St. Johns North Mainstem Duval 2204 Terrapin Creek

Intracoastal ICWW (Duval County; St 3 2 15-0721 Lower St. Johns Duval, St. Johns 2205C Waterway Johns County)

Intracoastal ICWW (Duval County; St 3 2 15-0722 Lower St. Johns Duval, St. Johns 2205C Waterway Johns County)

West Branch Blockhouse 4 2 20-0282 Lower St. Johns Trout River Duval 2210 Creek

St Johns River above 4 2 20-0283 Lower St. Johns North Mainstem Duval 2213A Mouth

St Johns River above 4 2 20-0284 Lower St. Johns North Mainstem Duval 2213A Mouth

1 2 03-2426 Lower St. Johns North Mainstem Unit Duval 2213C Stj Riv Ab Dames Pt St Johns River above 4 2 20-0285 Lower St. Johns North Mainstem Duval 2213C Dames Point

1 2 03-2429 Lower St. Johns North Mainstem Unit Duval 2213D Stj Riv Ab Trout Riv

3 2 15-0723 Lower St. Johns North Mainstem Unit Duval 2213EA Willow Branch

St Johns River above 3 2 15-0724 Lower St. Johns North Mainstem Unit Duval 2213F Piney Point

Deep Creek Unit Unnamed Drain to St. 2 2 09-2617 Lower St. Johns St. Johns 2213R LSJR Johns River

4 2 20-0286 Lower St. Johns Trout River Duval 2223 Trout River (Upper Reach)

4 2 20-0287 Lower St. Johns Trout River Duval 2223 Trout River (Upper Reach)

Ribault River (Marine 3 2 15-0727 Lower St. Johns Trout River Duval 2224A Segment)

Ribault River (Tidal 3 2 15-0728 Lower St. Johns Trout River Duval 2224B Segment)

Moncrief Creek (Marine 3 2 15-0730 Lower St. Johns Trout River Duval 2228A Portion)

Moncrief Creek (Marine 3 2 15-0731 Lower St. Johns Trout River Duval 2228A Portion)

Moncrief Creek (Marine 3 2 15-0732 Lower St. Johns Trout River Duval 2228A Portion)

Moncrief Creek 4 2 20-0288 Lower St. Johns Trout River Duval 2228B (Freshwater Portion)

1 2 03-2451 Lower St. Johns Trout River Duval 2232 Sixmile Creek Reach

1 2 03-2453 Lower St. Johns North Mainstem Unit Duval 2233 Long Branch 3 2 15-0733 Lower St. Johns North Mainstem Unit Duval 2233 Long Branch

Mount Pleasant Creek 3 2 15-0734 Lower St. Johns North Mainstem Unit Duval 2234B (Freshwater Segment)

4 2 20-0289 Lower St. Johns North Mainstem Duval 2235 Newcastle Creek

1 2 03-2455 Lower St. Johns Trout River Duval 2238 Little Sixmile Creek

4 2 20-0290 Lower St. Johns North Mainstem Duval 2239 Strawberry Creek

4 2 20-0291 Lower St. Johns North Mainstem Duval 2244 Cowhead Creek

Upper St. Marys Baker, Duval, 3 4 17-0417 Nassau - St. Marys 2245 Deep Creek River Unit Nassau

4 2 20-0292 Lower St. Johns North Mainstem Duval 2246 Jones Creek

1 2 03-2461 Lower St. Johns North Mainstem Unit Duval 2248 Gin House Creek

4 2 20-0293 Lower St. Johns Ortega River Clay,Duval 2249A Ortega River

4 2 20-0294 Lower St. Johns Ortega River Duval 2249B McGirts Creek

4 2 20-0295 Lower St. Johns Ortega River Duval 2249B McGirts Creek

1 2 03-2466 Lower St. Johns North Mainstem Unit Duval 2254 Red Bay Branch 4 2 20-0296 Lower St. Johns North Mainstem Duval 2254 Red Bay Branch

2 2 09-2660 Lower St. Johns North Mainstem Unit Duval 2256 Deer Creek

3 2 15-0735 Lower St. Johns North Mainstem Unit Duval 2256 Deer Creek

4 2 20-0297 Lower St. Johns Ortega River Duval 2262B Cedar River

Pottsburg Creek (Marine 3 2 15-0737 Lower St. Johns North Mainstem Unit Duval 2265D Segment)

Pottsburg Creek (Marine 4 2 20-0298 Lower St. Johns North Mainstem Duval 2265D Segment)

Intracoastal 1 2 03-2478 Lower St. Johns Duval 2270 Hogpen Creek Waterway

Intracoastal Hogpen Creek (Marine 3 2 15-0738 Lower St. Johns Duval 2270A Waterway Segment)

4 2 20-0299 Lower St. Johns North Mainstem Duval 2278 Silversmith Creek

Big Fishweir Creek 4 2 20-0300 Lower St. Johns Ortega River Duval 2280B (Marine Segment)

Big Fishweir Creek 4 2 20-0301 Lower St. Johns Ortega River Duval 2280B (Marine Segment)

Little Pottsburg Creek 3 2 15-0740 Lower St. Johns North Mainstem Unit Duval 2284A (Marine Portion)

Little Pottsburg Creek 3 2 15-0741 Lower St. Johns North Mainstem Unit Duval 2284A (Marine Portion) Little Pottsburg Creek 4 2 20-0302 Lower St. Johns North Mainstem Duval 2284B (Freshwater Portion)

Intracoastal 4 2 20-0303 Lower St. Johns Duval 2290 Cedar Swamp Creek Waterway

Intracoastal 2 2 09-2647 Lower St. Johns Duval 2302 Ryals Swamp Waterway

Wills Branch (South 4 2 20-0304 Lower St. Johns Ortega River Duval 2305 Prong)

4 2 20-0305 Lower St. Johns North Mainstem Duval 2306 New Rose Creek

4 2 20-0306 Lower St. Johns North Mainstem Duval 2308 Eagle Run

4 2 20-0307 Lower St. Johns North Mainstem Duval 2319 Bennett Branch

1 5 09-1159 Upper East Coast Tolomato River Unit St. Johns 2320 Guana River

1 2 03-2496 Lower St. Johns North Mainstem Unit Duval 2321 Christopher Branch

4 2 20-0308 Lower St. Johns Clay,Duval 2323 Yellow Water Creek

4 2 20-0309 Lower St. Johns Black Creek Clay,Duval 2323 Yellow Water Creek

Goodbys Creek 4 2 20-0310 Lower St. Johns North Mainstem Duval 2326A (Freshwater Segment) 4 2 20-0311 Lower St. Johns Ortega River Duval 2338 Unnamed Branch

4 2 20-0312 Lower St. Johns Julington Creek Duval 2351 Julington Creek

3 5 18-0331 Upper East Coast Halifax River Unit Volusia 2363A Halifax River

3 5 18-0332 Upper East Coast Halifax River Unit Volusia 2363A Halifax River

2 5 13-1350 Upper East Coast Halifax River Unit Volusia 2363B Halifax River

2 5 12-0109 Upper East Coast Halifax River Unit Volusia 2363C Tomoka Basin

3 5 18-0333 Upper East Coast Pellicer Creek Unit Flagler 2363D Palm Coast

ICWW (St Johns County; 2 5 13-1351 Upper East Coast Pellicer Creek Unit Flagler, St. Johns 2363EB Flagler County)

3 5 18-0334 Upper East Coast Pellicer Creek Unit Flagler 2363EC ICWW (Flagler County)

2 5 13-1352 Upper East Coast Pellicer Creek Unit St. Johns 2363F ICWW (St Johns County)

3 5 18-0335 Upper East Coast Tolomato River Unit St. Johns 2363I1 Tolomato River

Tolomato River (Shellfish 2 5 13-1353 Upper East Coast Tolomato River Unit St. Johns 2363I2 Portion) 3 5 18-0336 Upper East Coast Halifax River Unit Flagler, Volusia 2363J Palm Coast

4 2 20-0313 Lower St. Johns Julington Creek Duval 2370 Oldfield Creek

South Mainstem 1 2 03-2513 Lower St. Johns Duval 2382 Unnamed Drain Unit South Mainstem 1 2 03-2514 Lower St. Johns Duval 2385 Mandarin Drain Unit

2 2 09-2595 Lower St. Johns Black Creek Clay 2386A Black Creek (North Fork)

2 2 09-2596 Lower St. Johns Black Creek Clay 2389A Doctors Lake Drain

South Mainstem 2 2 09-2749 Lower St. Johns Clay 2405 Peters Branch Unit

Deep Creek (Marine 2 5 12-0120 Upper East Coast Tolomato River Unit St. Johns 2406C Segment)

Deep Creek (Marine 2 5 12-0121 Upper East Coast Tolomato River Unit St. Johns 2406C Segment) Black Creek Above St 1 2 04-0828 Lower St. Johns Black Creek Clay 2415A Johns River

2 2 09-2649 Lower St. Johns Julington Creek St. Johns 2419 Sampson Creek

1 2 03-2519 Lower St. Johns Black Creek Clay 2423 Mill Log Creek

4 2 20-0314 Lower St. Johns Black Creek Clay 2423 Mill Log Creek

1 2 03-2522 Lower St. Johns Black Creek Clay 2424 Bradley Creek

1 5 09-1177 Upper East Coast Tolomato River Unit St. Johns 2435 Capo Creek

1 5 09-1179 Upper East Coast Tolomato River Unit St. Johns 2442 Marshall Creek

1 5 09-1180 Upper East Coast Tolomato River Unit St. Johns 2442 Marshall Creek

2 2 09-2603 Lower St. Johns Black Creek Clay 2446 Bull Creek

1 5 09-1183 Upper East Coast Tolomato River Unit St. Johns 2457A St. Marks Pond Estuary

3 2 15-0749 Lower St. Johns Sixmile Creek St. Johns 2460 Mill Creek South Mainstem 2 2 09-2751 Lower St. Johns Clay 2464 Governor Creek Unit

1 5 09-1185 Upper East Coast Tolomato River Unit St. Johns 2468 Casa Cola Creek

1 5 09-1187 Upper East Coast Tolomato River Unit St. Johns 2470 Sombrero Creek

1 5 09-1188 Upper East Coast Tolomato River Unit St. Johns 2470 Sombrero Creek

1 5 09-1143 Upper East Coast Unit St. Johns 2472 Red House Branch

1 5 09-1190 Upper East Coast Tolomato River Unit St. Johns 2477 Ximanies Creek

1 5 09-1192 Upper East Coast Tolomato River Unit St. Johns 2483 Pancho Creek

2 5 12-0126 Upper East Coast Tolomato River Unit St. Johns 2487 Robinson Creek

3 5 18-0337 Upper East Coast Matanzas River Unit St. Johns 2499 Oyster Creek

3 5 18-0338 Upper East Coast Matanzas River Unit St. Johns 2499 Oyster Creek

3 4 17-0419 Pensacola Blackwater River Santa Rosa 24AB Blackwater River (Tidal)

Salt Run (Shellfish 2 5 13-1356 Upper East Coast Matanzas River Unit St. Johns 2502C Portion)

2 2 09-2629 Lower St. Johns Etonia Creek Clay 2509 Lake Geneva

2 2 09-2631 Lower St. Johns Etonia Creek Clay 2509H Lily Lake

2 2 09-2632 Lower St. Johns Etonia Creek Clay, Putnam 2511B Simms Creek

2 2 09-2633 Lower St. Johns Etonia Creek Clay, Putnam 2511B Simms Creek

Moses Creek (Marine 3 5 18-0339 Upper East Coast Matanzas River Unit St. Johns 2535A Segment)

Moses Creek (Freshwater 2 5 12-0134 Upper East Coast Matanzas River Unit St. Johns 2535B Segment)

2 2 09-2637 Lower St. Johns Etonia Creek Putnam 2543F Lake Ross

3 2 15-0751 Lower St. Johns Etonia Creek Putnam 2543F Lake Ross Deep Creek Unit 2 2 09-2621 Lower St. Johns St. Johns 2549 Deep Creek LSJR

4 2 20-0315 Lower St. Johns Deep Creek LSJR St. Johns 2549 Deep Creek

4 2 20-0316 Lower St. Johns Deep Creek LSJR St. Johns 2549 Deep Creek

4 2 20-0317 Lower St. Johns Deep Creek LSJR St. Johns 2549 Deep Creek

Unnamed Drain (Marine 2 5 12-0135 Upper East Coast Pellicer Creek Unit St. Johns 2550A Segment)

Deep Creek Unit 2 2 09-2623 Lower St. Johns Putnam, St. Johns 2555 Cracker Branch LSJR

Deep Creek Unit 2 2 09-2624 Lower St. Johns Putnam, St. Johns 2555 Cracker Branch LSJR

Deep Creek Unit 2 2 09-2625 Lower St. Johns Putnam, St. Johns 2555 Cracker Branch LSJR Deep Creek Unit 2 2 09-2627 Lower St. Johns St. Johns 2561 Unnamed Ditches LSJR

Deep Creek Unit 3 2 15-0752 Lower St. Johns St. Johns 2561 Unnamed Ditches LSJR

4 2 20-0318 Lower St. Johns Deep Creek LSJR St. Johns 2561 Unnamed Ditches South Mainstem 3 2 15-0754 Lower St. Johns Putnam, St. Johns 2569 West Run Interceptor D Unit

4 2 20-0319 Lower St. Johns South Mainstem Putnam,St. Johns 2569 West Run Interceptor D

4 2 20-0320 Lower St. Johns South Mainstem Putnam,St. Johns 2569 West Run Interceptor D

Deep Creek Unit 1 2 03-2532 Lower St. Johns St. Johns 2571 Unnamed Ditch LSJR

Deep Creek Unit 3 2 15-0755 Lower St. Johns St. Johns 2571 Unnamed Ditch LSJR

2 5 12-0137 Upper East Coast Pellicer Creek Unit St. Johns 2573 Unnamed Drain

2 5 12-0139 Upper East Coast Pellicer Creek Unit Flagler 2577 Pringle Branch

South Mainstem 3 2 15-0756 Lower St. Johns Putnam 2578 Dog Branch Unit

South Mainstem 3 2 15-0757 Lower St. Johns Putnam 2578 Dog Branch Unit

3 5 18-0340 Upper East Coast Pellicer Creek Unit Flagler, St. Johns 2580A Pellicer Creek

3 5 18-0341 Upper East Coast Pellicer Creek Unit Flagler, St. Johns 2580A Pellicer Creek

3 5 18-0342 Upper East Coast Pellicer Creek Unit Flagler, St. Johns 2580B Pellicer Creek

3 5 18-0343 Upper East Coast Pellicer Creek Unit Flagler, St. Johns 2580B Pellicer Creek 4 2 20-0321 Lower St. Johns Etonia Creek Putnam 2582 Lake Suggs

3 2 15-0758 Lower St. Johns Etonia Creek Putnam 2582A Rowan Lake

4 2 20-0322 Lower St. Johns Etonia Creek Putnam 2582A Rowan Lake

4 2 20-0323 Lower St. Johns Etonia Creek Putnam 2582A Rowan Lake

South Mainstem 1 2 03-2535 Lower St. Johns Putnam 2583 Cow Branch Unit

South Mainstem 1 2 03-2539 Lower St. Johns Putnam 2592 Mill Branch Unit

South Mainstem 3 2 15-0760 Lower St. Johns Putnam 2599 Twomile Creek Unit

1 2 03-2542 Lower St. Johns Crescent Lake Putnam 2606A Dunns Creek

3 2 15-0761 Lower St. Johns Crescent Lake Putnam 2606A Dunns Creek

3 5 18-0344 Upper East Coast Pellicer Creek Unit Flagler 2609A St Joe Canal

3 5 18-0345 Upper East Coast Pellicer Creek Unit Flagler 2609A St Joe Canal

3 2 15-0764 Lower St. Johns Crescent Lake Flagler 2610 Unnamed Canal

4 2 20-0324 Lower St. Johns Crescent Lake Flagler 2615 Bull Creek Ditches 3 2 15-0765 Lower St. Johns Crescent Lake Flagler 2615A Dead Lake

3 2 15-0766 Lower St. Johns Crescent Lake Flagler 2615A Dead Lake

Haw Creek Above 2 2 09-2609 Lower St. Johns Crescent Lake Flagler 2622A Crescent Lake

Haw Creek above 4 2 20-0325 Lower St. Johns Crescent Lake Flagler 2622A Crescent Lake

Haw Creek above 4 2 20-0326 Lower St. Johns Crescent Lake Flagler 2622A Crescent Lake

Haw Creek above 4 2 20-0327 Lower St. Johns Crescent Lake Flagler 2622A Crescent Lake

2 2 09-2611 Lower St. Johns Crescent Lake Flagler 2628 Sweetwater Branch

2 2 09-2612 Lower St. Johns Crescent Lake Flagler, Volusia 2630A Little Haw Creek

2 2 09-2613 Lower St. Johns Crescent Lake Flagler 2630B Lake Disston

2 5 12-0146 Upper East Coast Halifax River Unit Flagler, Volusia 2635 Groover Branch 2 5 12-0148 Upper East Coast Halifax River Unit Volusia 2640 Unnamed Branch

3 5 18-0346 Upper East Coast Halifax River Unit Volusia 2641 Unnamed Branch

3 5 18-0347 Upper East Coast Halifax River Unit Volusia 2645 Mizners Branch

3 5 18-0348 Upper East Coast Halifax River Unit Volusia 2673 Tributary to Spruce Creek

3 5 18-0349 Upper East Coast Halifax River Unit Volusia 2673 Tributary to Spruce Creek

3 5 18-0350 Upper East Coast Halifax River Unit Volusia 2674 Spruce Creek

2 5 13-1358 Upper East Coast Halifax River Unit Volusia 2674A Spruce Creek

1 5 09-1133 Upper East Coast Halifax River Unit Volusia 2678 Turnbull Bay

1 5 09-1135 Upper East Coast Halifax River Unit Volusia 2678 Turnbull Bay 3 5 18-0351 Upper East Coast Halifax River Unit Volusia 2681 Glencoe Ditches

3 5 18-0352 Upper East Coast Halifax River Unit Volusia 2681 Glencoe Ditches

3 5 18-0353 Upper East Coast Halifax River Unit Volusia 2681 Glencoe Ditches

2 1 09-2022 Ocklawaha Alachua 2688 Hatchet Creek

2 1 09-2024 Ocklawaha Orange Creek Alachua 2695 Little Hatchet Creek

4 1 19-0576 Ocklawaha Orange Creek Alachua 2696 Possum Creek

4 1 19-0577 Ocklawaha Orange Creek Alachua 2700 Hammocks Lake

4 1 19-0578 Ocklawaha Orange Creek Alachua 2700 Hammocks Lake

4 1 19-0579 Ocklawaha Orange Creek Alachua 2700 Hammocks Lake 4 1 19-0580 Ocklawaha Orange Creek Alachua 2700 Hammocks Lake

4 1 19-0581 Ocklawaha Orange Creek Alachua 2705A Prairie Creek

4 1 19-0582 Ocklawaha Orange Creek Alachua 2705A Prairie Creek

4 1 19-0583 Ocklawaha Orange Creek Alachua 2705A Prairie Creek

4 1 19-0584 Ocklawaha Orange Creek Alachua 2705A Prairie Creek

4 1 19-0585 Ocklawaha Orange Creek Alachua 2706 Lake Moon

3 1 13-0142 Ocklawaha Orange Creek Alachua 2709 Sunland Drain

3 1 13-0143 Ocklawaha Orange Creek Alachua 2710 Unnamed Drain

2 1 09-2028 Ocklawaha Orange Creek Alachua, Putnam 2713 Little Orange Creek 4 1 19-0586 Ocklawaha Orange Creek Alachua, Putnam 2713D Little Orange Lake

3 1 13-0144 Ocklawaha Orange Creek Alachua 2717 Kanapaha Lake

4 1 19-0587 Ocklawaha Orange Creek Alachua 2718A Tumblin Creek

2 1 09-2032 Ocklawaha Orange Creek Alachua 2718B Bevens Arm

3 1 13-0146 Ocklawaha Orange Creek Alachua 2719 Lake Alice Outlet

2 1 09-2034 Ocklawaha Orange Creek Alachua 2720 Alachua Sink Outlet 2 1 09-2035 Ocklawaha Orange Creek Alachua 2720A Alachua Sink

4 1 19-0588 Ocklawaha Orange Creek Alachua 2722A Boulware Springs

2 1 09-2037 Ocklawaha Orange Creek Alachua 2733 Camps Canal Reach

4 1 19-0589 Ocklawaha Orange Creek Alachua 2733 Camps Canal

4 1 19-0590 Ocklawaha Orange Creek Alachua 2733 Camps Canal 4 1 19-0591 Ocklawaha Orange Creek Alachua 2733 Camps Canal

Marshall Swamp above 4 1 19-0592 Ocklawaha Marion 2740D Unit Daisy Creek

Marshall Swamp Ocklawaha River above 4 1 19-0593 Ocklawaha Marion 2740D Unit Daisy Creek

3 1 13-0148 Ocklawaha Orange Creek Alachua, Marion 2749B Orange Lake Drain

3 1 13-0149 Ocklawaha Orange Creek Alachua 2751 Lochloosa Slough

Rodman Reservoir 4 1 19-0594 Ocklawaha Marion 2769 Daisy Creek Unit

Marshall Swamp 4 1 19-0595 Ocklawaha Marion 2774 Half Mile Creek Unit

Marshall Swamp 4 1 19-0596 Ocklawaha Marion 2790B Little Unit Marshall Swamp 4 1 19-0597 Ocklawaha Marion 2790B Little Lake Weir Unit

Marshall Swamp 4 1 19-0598 Ocklawaha Marion 2790B Little Lake Weir Unit

3 1 13-0152 Ocklawaha Lake Harris Unit Lake 2815 Farm Ditches

4 1 19-0599 Ocklawaha Lake Griffin Unit Lake 2825A Silver Lake

4 1 19-0600 Ocklawaha Lake, Orange 2835D Lake Apopka

Blue Springs (Lake 4 1 19-0601 Ocklawaha Lake Harris Unit Lake 2838C County)

Blue Springs (Lake 4 1 19-0602 Ocklawaha Lake Harris Unit Lake 2838C County)

4 1 19-0603 Ocklawaha Lake Harris Unit Lake 2838D Holiday Springs

Choctawhatchee - Choctawhatchee Holmes, 2 3 10-0473 286 Open Creek St. Andrew River Washington

2 1 09-2053 Ocklawaha Palatlakaha River Lake 2883 Little Creek St Johns River Above 2 3 10-0324 Upper St. Johns Tosohatchee Unit Brevard, Orange 28935 Puzzle Lake (South Segment)

St Johns River above 3 3 16-0723 Upper St. Johns Tosohatchee Unit Brevard, Orange 28935 Puzzle Lake (South Segment)

Blue Cypress Creek 3 3 16-0724 Upper St. Johns 28938 Blue Cypress Marsh Unit

St Johns River Above 2 3 10-0293 Upper St. Johns Puzzle Lake Unit Brevard, Orange 2893I Puzzle Lake

St Johns River Above 2 3 10-0295 Upper St. Johns Puzzle Lake Unit Brevard, Orange 2893I Puzzle Lake

St Johns River above 3 3 16-0725 Upper St. Johns Puzzle Lake Unit Brevard, Orange 2893I Puzzle Lake

St. Johns Marsh 2 3 10-0309 Upper St. Johns Brevard 2893O1 Lake Washington Drain Unit

St. Johns Marsh 3 3 16-0726 Upper St. Johns Brevard 2893O1 Lake Washington Drain Unit

St. Johns Marsh St Johns River above Lake 3 3 16-0727 Upper St. Johns Brevard 2893P Unit Washington

St. Johns Marsh St Johns River above Lake 3 3 16-0728 Upper St. Johns Brevard 2893P Unit Washington

3 2 15-0771 Middle St. Johns Lake Woodruff Unit Volusia 2893U Lake Beresford

Blue Cypress Creek 4 2 20-0628 Upper St. Johns Indian River 2893V Unit

St. Johns Marsh 2 3 10-0316 Upper St. Johns Brevard 2893X1 Sawgrass Lake Drain Unit

3 3 16-0729 Upper St. Johns Unit Brevard, Osceola 2893Y1 Lake Winder Drain 3 3 16-0730 Upper St. Johns Lake Poinsett Unit Brevard, Osceola 2893Y1 Lake Winder Drain

Louise Lake (Lower 4 2 20-0328 Middle St. Johns Volusia 2902 Segment)

Louise Lake (Lower 4 2 20-0329 Middle St. Johns Lake George Volusia 2902 Segment)

Louise Lake (Lower 4 2 20-0330 Middle St. Johns Lake George Volusia 2902 Segment)

Alexander Springs 3 2 15-0774 Middle St. Johns Lake 2918A Alexander Springs Drain Creek

4 2 20-0331 Middle St. Johns Lake Woodruff Volusia 2921D1 Tick Island Mud Lake

4 2 20-0332 Middle St. Johns Lake Woodruff Volusia 2921D1 Tick Island Mud Lake

4 2 20-0333 Middle St. Johns Lake Woodruff Volusia 2921D1 Tick Island Mud Lake 4 2 20-0334 Middle St. Johns Lake Woodruff Volusia 2921F Spring Garden Creek

Indian River 3 5 18-0269 Brevard, Volusia 2924 Mosquito Lagoon Lagoon Unit

Indian River Mosquito Lagoon 3 5 18-0270 Brevard, Volusia 2924 Mosquito Lagoon Lagoon Unit

Indian River Mosquito Lagoon 3 5 18-0271 Brevard, Volusia 2924 Mosquito Lagoon Lagoon Unit

Indian River Mosquito Lagoon Mosquito Lagoon 2 5 13-1335 Volusia 2924B1 Lagoon Unit (Shellfish Portion)

Indian River Mosquito Lagoon Mosquito Lagoon 3 5 18-0272 Volusia 2924B1 Lagoon Unit (Shellfish Portion)

Indian River Mosquito Lagoon Mosquito Lagoon 3 5 18-0273 Volusia 2924B1 Lagoon Unit (Shellfish Portion) Indian River Mosquito Lagoon 3 5 18-0274 Volusia 2924B2 Mosquito Lagoon Lagoon Unit

Indian River Mosquito Lagoon 3 5 18-0275 Volusia 2924B2 Mosquito Lagoon Lagoon Unit

2 2 09-2253 Middle St. Johns Lake 2934 Tracy Canal

Indian River North Indian River Turnbull Creek (Marine 2 5 12-0293 Volusia 2942A Lagoon Lagoon Unit Segment)

Indian River North Indian River Turnbull Creek (Marine 3 5 18-0276 Volusia 2942A Lagoon Lagoon Unit Segment)

Deep Creek Unit 2 2 09-2181 Middle St. Johns Volusia 2952 Cow Creek MSJR

Indian River North Central Indian Indian River Above 2 5 13-1336 Brevard 2963A1 Lagoon River Lagoon Sebastian Inlet

Indian River North Central Indian Indian River above 3 5 18-0277 Brevard 2963A1 Lagoon River Lagoon Sebastian Inlet

Indian River North Central Indian Indian River above 3 5 18-0278 Brevard 2963B1 Lagoon River Lagoon Melbourne Causeway Indian River North Central Indian Indian River above 3 5 18-0279 Brevard 2963B1 Lagoon River Lagoon Melbourne Causeway

Indian River North Indian River Indian River Above 2 5 13-1338 Brevard 2963C1 Lagoon Lagoon Unit Melbourne Causeway

Indian River North Indian River Indian River Above 520 2 5 13-1339 Brevard 2963D1 Lagoon Lagoon Unit Causeway

Indian River North Indian River Indian River Above Nasa 2 5 13-1340 Brevard 2963EA Lagoon Lagoon Unit Causeway

3 3 16-0731 Upper St. Johns Puzzle Lake Unit Seminole, Volusia 2964B Puzzle Lake

2 2 09-2239 Middle St. Johns Unit Seminole 2973 Deforest Lake Outlet

2 2 09-2240 Middle St. Johns Lake Monroe Unit Seminole 2973 Deforest Lake Outlet

2 2 09-2202 Middle St. Johns Seminole 2982 Phelps Creek

4 2 20-0335 Middle St. Johns Lake Jesup Seminole 2984 Six Mile Creek

1 2 03-2589 Middle St. Johns Lake Jesup Seminole 2985 Chub Creek

2 2 09-2204 Middle St. Johns Lake Jesup Seminole 2985 Chub Creek

3 2 15-0784 Middle St. Johns Lake Jesup Seminole 2986F Greenwood Lake 4 2 20-0336 Middle St. Johns Lake Jesup Seminole 2986F Greenwood Lake

4 2 20-0337 Middle St. Johns Wekiva River Seminole 2987Y Palm Springs

4 2 20-0338 Middle St. Johns Wekiva River Seminole 2987Z Sanlando Spring

4 2 20-0339 Middle St. Johns Lake Jesup Seminole 2990 Salt Creek

Econlockhatchee Osceola,Seminole,O 4 2 20-0340 Middle St. Johns 2991 River range

4 2 20-0341 Middle St. Johns Lake Jesup Seminole 2992 Black Hammock

4 2 20-0342 Middle St. Johns Lake Jesup Seminole 2994K Lake Concord

4 2 20-0343 Middle St. Johns Lake Jesup Seminole 2994K Lake Concord

4 2 20-0344 Middle St. Johns Lake Jesup Seminole 2995 Lake Charm

4 2 20-0345 Middle St. Johns Lake Jesup Seminole 2995 Lake Charm 4 2 20-0346 Middle St. Johns Lake Jesup Seminole 2995 Lake Charm

4 2 20-0347 Middle St. Johns Lake Jesup Seminole 2996 Sweetwater Creek

Howell Creek Below Lake 2 2 09-2213 Middle St. Johns Lake Jesup Seminole 2997 Howell

Howell Creek above Lake 4 2 20-0348 Middle St. Johns Lake Jesup Seminole,Orange 2997A Howell

4 2 20-0349 Middle St. Johns Lake Jesup Orange 2997L Lake Winyah

4 2 20-0350 Middle St. Johns Lake Jesup Orange 2997L Lake Winyah

2 2 09-2223 Middle St. Johns Lake Jesup Orange 2997Q Lake Dot

Lake Gem (Orange 3 2 15-0792 Middle St. Johns Lake Jesup Orange 2997V County)

3 2 15-0796 Middle St. Johns Lake Jesup Seminole 2999 Bear Creek

4 2 20-0351 Middle St. Johns Lake Jesup Seminole 2999B Noname Lake 4 2 20-0352 Middle St. Johns Lake Jesup Seminole 2999B Noname Lake

4 2 20-0353 Middle St. Johns Lake Jesup Seminole 2999B Noname Lake

Econlockhatchee Little Econlockhatchee 4 2 20-0354 Middle St. Johns Seminole,Orange 3001 River River

4 2 20-0355 Middle St. Johns Wekiva River Orange 3002D Starke Lake

4 2 20-0356 Middle St. Johns Wekiva River Orange 3002D Starke Lake

4 2 20-0357 Middle St. Johns Wekiva River Orange 3002G Lake Lotta

3 2 15-0802 Middle St. Johns Wekiva River Orange 3002Q Kasey Lake 4 2 20-0358 Middle St. Johns Wekiva River Orange 3002Q Kasey Lake

4 2 20-0359 Middle St. Johns Wekiva River Orange 3002Q Kasey Lake

4 2 20-0360 Middle St. Johns Wekiva River Orange 3002Q Kasey Lake

4 2 20-0361 Middle St. Johns Wekiva River Orange 3002Q Kasey Lake

4 2 20-0362 Middle St. Johns Wekiva River Orange 3002R Kelly Lake

4 2 20-0363 Middle St. Johns Wekiva River Orange 3004R Lake Fairhope

4 2 20-0364 Middle St. Johns Wekiva River Orange 3004R Lake Fairhope 4 2 20-0365 Middle St. Johns Wekiva River Orange 3004R Lake Fairhope

4 2 20-0366 Middle St. Johns Wekiva River Orange 3004R Lake Fairhope

3 2 15-0810 Middle St. Johns Lake Jesup Orange, Seminole 3009G Bear Gulley Lake Drain

3 2 15-0811 Middle St. Johns Wekiva River Orange 3011A Lake Weston

2 3 10-0327 Upper St. Johns Tosohatchee Unit Brevard 3013 Unnamed Slough

Econlockhatchee 4 2 20-0367 Middle St. Johns Seminole,Orange 3014 Crane Strand Drain River

Econlockhatchee 2 2 09-2188 Middle St. Johns Orange 3021 Unnamed Branch River

Econlockhatchee 4 2 20-0368 Middle St. Johns Orange 3023 Crane Strand River

Econlockhatchee 1 2 03-2635 Middle St. Johns Orange 3023A Lake Baldwin Outfall River

Econlockhatchee 1 2 03-2640 Middle St. Johns Orange 3024A Trib. to Little Econ. River River

Indian River North Indian River 2 5 12-0301 Brevard 3028 Addison Creek Lagoon Lagoon Unit

Econlockhatchee Lake Dover - Lake C - 4 2 20-0369 Middle St. Johns Orange 3036B8 River Lake Santiago Econlockhatchee Lake Dover - Lake C - 4 2 20-0370 Middle St. Johns Orange 3036B8 River Lake Santiago

Econlockhatchee 4 2 20-0371 Middle St. Johns Orange 3037 Avalon Branch River

3 3 16-0732 Upper St. Johns Tosohatchee Unit Orange 3042 Jim Creek

Indian River 3 5 18-0280 Unit Brevard 3044A Newfound Harbor Lagoon

Econlockhatchee 4 2 20-0372 Middle St. Johns Orange 3046 Unnamed Drain River

Econlockhatchee 4 2 20-0373 Middle St. Johns Orange 3046 Unnamed Drain River

Indian River Banana River below 520 3 5 18-0281 Banana River Unit Brevard 3057A Lagoon Causeway

Indian River Banana River above 520 3 5 18-0282 Banana River Unit Brevard 3057B Lagoon Causeway

Indian River North Central Indian 1 5 09-1219 Brevard 3082 Lagoon River Lagoon

Indian River North Central Indian 3 5 18-0283 Brevard 3085 Crane Creek Lagoon River Lagoon

Indian River North Central Indian 2 5 12-0305 Brevard 3085A Crane Creek Lagoon River Lagoon Indian River North Central Indian 3 5 18-0284 Brevard 3087 Elbow Creek Lagoon River Lagoon

Interbasin Diversion 2 3 10-0281 Upper St. Johns Brevard 3090 Drained Farmland Unit

Interbasin Diversion Melbourne-Tillman (C-1) 3 3 16-0733 Upper St. Johns Brevard 3090 Unit Canal

Indian River North Central Indian Goat Creek (Freshwater 2 5 12-0314 Brevard 3107B Lagoon River Lagoon Segment)

St. Johns Marsh 3 3 16-0734 Upper St. Johns Brevard 3108A2 South Mormon Canal Unit

St. Johns Marsh Brevard, Indian 2 3 10-0319 Upper St. Johns 3108B Marsh Unit River

St. Johns Marsh Brevard, Indian 3 3 16-0735 Upper St. Johns 3108B C-40 (Sixmile Marsh) Unit River

St. Johns Marsh Brevard, Indian 3 3 16-0736 Upper St. Johns 3108B C-40 (Sixmile Marsh) Unit River

Indian River North Central Indian 2 5 12-0315 Brevard 3119 Trout Creek Lagoon River Lagoon

St. Johns Marsh 3 3 16-0737 Upper St. Johns Brevard 3125 Wolf Creek Canal Unit

St. Johns Marsh 3 3 16-0738 Upper St. Johns Brevard 3125 Wolf Creek Canal Unit

St. Johns Marsh 2 3 10-0322 Upper St. Johns Brevard, Osceola 3127 Wolf Creek Unit

Indian River South Central Indian Brevard, Indian St. Sebastian River above 3 5 18-0285 3129A Lagoon River Lagoon River Blue Cypress Creek 3 3 16-0739 Upper St. Johns Indian River 3140 Lake Kenansville Unit

Blue Cypress Creek 3 3 16-0740 Upper St. Johns Indian River 3140 Lake Kenansville Unit

Blue Cypress Creek 3 3 16-0741 Upper St. Johns Indian River 3140 Lake Kenansville Unit

Indian River South Central Indian 1 5 09-1257 Indian River 3147 North Canal Lagoon River Lagoon

Indian River South Central Indian 3 5 18-0286 Indian River 3147 North Canal Lagoon River Lagoon

Indian River South Central Indian 2 5 12-0324 Indian River 3153A Main Canal Lagoon River Lagoon

Fort Drum Creek Indian River, 2 3 10-0278 Upper St. Johns 3154 Fort Drum Creek Unit Okeechobee

Indian River South Central Indian 1 5 09-1261 Indian River 3158 South Canal Lagoon River Lagoon

St. Lucie - Okeechobee, St. C-25 Canal West (St. 2 2 09-1697 C-25 3160 Loxahatchee Lucie Johns Marsh)

Fort Pierce Farm Canal Indian River 3 5 18-0290 C-25 St. Lucie 3163 (Belcher Canal/Taylor Lagoon Creek)

Fort Pierce Farm Canal Indian River 3 5 18-0291 C-25 St. Lucie 3163 (Belcher Canal/Taylor Lagoon Creek) St. Lucie - 1 2 03-2648 C-25 St. Lucie 3163B C-25 East Segment Loxahatchee

Indian River 3 5 18-0292 C-25 St. Lucie 3163B C-25 East Segment Lagoon

St. Lucie - 4 2 20-0374 Coastal St. Lucie 3166 Moore Creek Loxahatchee

Upper Kissimmee 2 4 10-3163 Kissimmee River Orange 3168B Boggy Creek Planning Unit

Upper Kissimmee 3 4 17-0342 Kissimmee River Orange 3168E Lake Anderson Planning Unit

Upper Kissimmee 3 4 17-0343 Kissimmee River Orange 3168F Lake Bass Planning Unit

Upper Kissimmee 3 4 17-0344 Kissimmee River Orange 3168F Lake Bass Planning Unit

Upper Kissimmee Lake Warren (Lake Mare 3 4 17-0345 Kissimmee River Orange 3168Q Planning Unit Prairie)

Upper Kissimmee Lake Warren (Lake Mare 3 4 17-0346 Kissimmee River Orange 3168Q Planning Unit Prairie) Upper Kissimmee Lake Warren (Lake Mare 3 4 17-0347 Kissimmee River Orange 3168Q Planning Unit Prairie)

Upper Kissimmee 3 4 17-0348 Kissimmee River Orange 3168W3 Lake Wade Planning Unit

Upper Kissimmee 3 4 17-0349 Kissimmee River Orange 3168W3 Lake Wade Planning Unit

Upper Kissimmee 3 4 17-0350 Kissimmee River Orange 3168W3 Lake Wade Planning Unit

Upper Kissimmee 3 4 17-0351 Kissimmee River Orange 3168W4 Lake of The Woods Planning Unit

Upper Kissimmee 3 4 17-0352 Kissimmee River Orange 3168W4 Lake of The Woods Planning Unit

Upper Kissimmee 3 4 17-0353 Kissimmee River Orange 3168W6 Lake Warren Planning Unit Upper Kissimmee 3 4 17-0354 Kissimmee River Orange 3168W7 Lake Bumby Planning Unit

Upper Kissimmee 3 4 17-0355 Kissimmee River Orange 3168W7 Lake Bumby Planning Unit

Upper Kissimmee 3 4 17-0356 Kissimmee River Orange 3168W7 Lake Bumby Planning Unit

Upper Kissimmee 3 4 17-0357 Kissimmee River Orange 3168W7 Lake Bumby Planning Unit

Upper Kissimmee 3 4 17-0358 Kissimmee River Orange 3168X2 Hourglass Lake Planning Unit

Upper Kissimmee 3 4 17-0359 Kissimmee River Orange 3168X4 Lake Rabama Planning Unit

Upper Kissimmee 2 4 10-3172 Kissimmee River Orange 3168X5 Lake Condel Planning Unit

Upper Kissimmee 3 4 17-0360 Kissimmee River Orange 3168X5 Lake Condel Planning Unit

Upper Kissimmee 3 4 17-0361 Kissimmee River Orange 3168X5 Lake Condel Planning Unit

Upper Kissimmee 3 4 17-0362 Kissimmee River Orange 3168X5 Lake Condel Planning Unit Upper Kissimmee 3 4 17-0363 Kissimmee River Orange 3168X5 Lake Condel Planning Unit

Upper Kissimmee 3 4 17-0364 Kissimmee River Orange 3168X8 Lake Angel Planning Unit

Upper Kissimmee 3 4 17-0365 Kissimmee River Orange 3168X8 Lake Angel Planning Unit

Upper Kissimmee 3 4 17-0366 Kissimmee River Orange 3168Y Lake Lancaster Planning Unit

Upper Kissimmee 3 4 17-0367 Kissimmee River Orange 3168Y Lake Lancaster Planning Unit

Upper Kissimmee 3 4 17-0368 Kissimmee River Orange 3168Y Lake Lancaster Planning Unit

Upper Kissimmee Lake Como (Orange 3 4 17-0369 Kissimmee River Orange 3168Y2 Planning Unit County) Upper Kissimmee 3 4 17-0370 Kissimmee River Orange 3168Y3 Lake Greenwood Planning Unit

Upper Kissimmee 3 4 17-0371 Kissimmee River Orange 3168Y4 Lake Davis Planning Unit

Upper Kissimmee 3 4 17-0372 Kissimmee River Orange 3168Y4 Lake Davis Planning Unit

Upper Kissimmee 3 4 17-0373 Kissimmee River Orange 3168Y4 Lake Davis Planning Unit

Upper Kissimmee 3 4 17-0374 Kissimmee River Orange 3168Y6 Lake Lurna Planning Unit

Upper Kissimmee 3 4 17-0375 Kissimmee River Orange 3168Y8 Lake Weldona Planning Unit

Upper Kissimmee 3 4 17-0376 Kissimmee River Orange 3168Z3 Lake Arnold Planning Unit

Upper Kissimmee 3 4 17-0377 Kissimmee River Orange 3168Z3 Lake Arnold Planning Unit Upper Kissimmee 3 4 17-0378 Kissimmee River Orange 3168Z3 Lake Arnold Planning Unit

Upper Kissimmee 3 4 17-0379 Kissimmee River Orange 3168Z4 Lake Giles Planning Unit

Upper Kissimmee 3 4 17-0380 Kissimmee River Orange 3168Z9 Lake Lawsona Planning Unit

Upper Kissimmee 3 4 17-0381 Kissimmee River Orange, Osceola 3169A Planning Unit

Upper Kissimmee 3 4 17-0382 Kissimmee River Orange 3169C Big Sand Lake Planning Unit

Upper Kissimmee 3 4 17-0383 Kissimmee River Orange 3169G3 Lake Fran Planning Unit

Upper Kissimmee 3 4 17-0384 Kissimmee River Orange 3169G3 Lake Fran Planning Unit

Upper Kissimmee 3 4 17-0385 Kissimmee River Orange 3169G3 Lake Fran Planning Unit Upper Kissimmee 3 4 17-0386 Kissimmee River Orange 3169G4 Lake Kozart Planning Unit

Upper Kissimmee 3 4 17-0387 Kissimmee River Orange 3169G4 Lake Kozart Planning Unit

Upper Kissimmee 3 4 17-0388 Kissimmee River Orange 3169G4 Lake Kozart Planning Unit

Upper Kissimmee 3 4 17-0389 Kissimmee River Orange 3169G5 Lake Walker Planning Unit

Upper Kissimmee 3 4 17-0390 Kissimmee River Orange 3169G5 Lake Walker Planning Unit

Upper Kissimmee 3 4 17-0391 Kissimmee River Orange 3169G5 Lake Walker Planning Unit

Upper Kissimmee 3 4 17-0392 Kissimmee River Orange 3169G6 Lake Richmond Planning Unit Upper Kissimmee 3 4 17-0393 Kissimmee River Orange 3169G6 Lake Richmond Planning Unit

Upper Kissimmee 3 4 17-0394 Kissimmee River Orange 3169G6 Lake Richmond Planning Unit

Upper Kissimmee 3 4 17-0395 Kissimmee River Orange 3169G8 Lake Beardall Planning Unit

Upper Kissimmee 3 4 17-0396 Kissimmee River Orange 3169Q Rock Lake Planning Unit

Upper Kissimmee 3 4 17-0397 Kissimmee River Orange 3169T Lake Sandy Planning Unit

Upper Kissimmee 3 4 17-0399 Kissimmee River Orange 3170I Lake Hickorynut Planning Unit

Upper Kissimmee 2 4 10-3189 Kissimmee River Orange 3170J Cypress Creek Planning Unit

Upper Kissimmee 3 4 17-0400 Kissimmee River Orange 3170J Upper Cypress Creek Planning Unit

Upper Kissimmee 1 4 06-0547 Kissimmee River Osceola 3170K Davenport Creek Planning Unit Upper Kissimmee 3 4 17-0401 Kissimmee River Orange 3170Q Lake Butler Planning Unit

Upper Kissimmee 3 4 17-0402 Kissimmee River Orange 3171 Lake Hart Planning Unit

Upper Kissimmee 3 4 17-0403 Kissimmee River Orange 3171A Lake Mary Jane Planning Unit

Upper Kissimmee 1 4 06-0552 Kissimmee River Orange 3171C Red Lake Planning Unit

Upper Kissimmee East 3 4 17-0404 Kissimmee River Orange, Osceola 3172C Planning Unit Drain

Upper Kissimmee Lake Tohopekaliga Drain 3 4 17-0405 Kissimmee River Osceola 3173C Planning Unit (South Segment)

Upper Kissimmee Lake Tohopekaliga Drain 3 4 17-0406 Kissimmee River Osceola 3173C Planning Unit (South Segment)

Upper Kissimmee 3 4 17-0407 Kissimmee River Osceola, Polk 3186A Kissimmee River Planning Unit

Lower Kissimmee 2 4 10-3204 Kissimmee River Highlands, Polk 3186D Eightmile Slough Planning Unit

Lower Kissimmee 2 4 10-3205 Kissimmee River Polk 3186E Packingham Slough Planning Unit

Lower Kissimmee 2 4 10-3206 Kissimmee River Osceola 3186G Blanket Bay Slough Planning Unit

Lower Kissimmee 2 4 10-3207 Kissimmee River Osceola 3186G Blanket Bay Slough Planning Unit Lower Kissimmee 3 4 17-0408 Kissimmee River Osceola 3186G Blanket Bay Slough Planning Unit

Lower Kissimmee 3 4 17-0409 Kissimmee River Osceola 3186G Blanket Bay Slough Planning Unit

Lower Kissimmee Kissimmee River Below S- 2 4 10-3208 Kissimmee River Highlands, Polk 3187D Planning Unit 65A

Lower Kissimmee 2 4 10-3209 Kissimmee River Okeechobee 3188B Farm Area Planning Unit

St. Lucie - 1 2 03-2651 Coastal St. Lucie 3190 North Coastal Loxahatchee

Lower Kissimmee 1 4 06-0524 Kissimmee River Okeechobee 3192C Oak Creek Planning Unit

Lower Kissimmee 2 4 10-3210 Kissimmee River Okeechobee 3192C Oak Creek Planning Unit

Lower Kissimmee 2 4 10-3211 Kissimmee River Okeechobee 3192C Oak Creek Planning Unit

Lower Kissimmee 3 4 17-0410 Kissimmee River Okeechobee 3192C Oak Creek Planning Unit

Lower Kissimmee 3 4 17-0411 Kissimmee River Okeechobee 3192C Oak Creek Planning Unit

St. Lucie - 4 2 20-0375 Coastal Martin 3193 St Lucie River Loxahatchee

St. Lucie - 2 2 09-1702 Coastal Martin 3193A Roosevelt Bridge Loxahatchee

St. Lucie - 1 2 03-2656 North St. Lucie St. Lucie 3194 North St.Lucie Loxahatchee

St. Lucie - 4 2 20-0376 North St. Lucie St. Lucie 3194 St Lucie River (North Fork) Loxahatchee

St. Lucie - 1 2 03-2660 North St. Lucie Martin, St. Lucie 3194B St. Lucie Loxahatchee St. Lucie - 2 2 09-1732 North St. Lucie Martin, St. Lucie 3194C Savannas Loxahatchee

St. Lucie - 4 2 20-0377 North St. Lucie St. Lucie 3194D Fivemile Creek Loxahatchee

Northwest Lake 2 4 10-3083 Okeechobee Highlands 3198 C-41A Planning Unit

Northwest Lake 3 4 17-0291 Fisheating Creek Okeechobee Highlands 3198 C-41A Planning Unit

2 1 09-2072 CTP Complex Okeechobee 3199A Turkey Slough

Chandler Hammock 2 1 09-2073 Lake Okeechobee CTP Complex Okeechobee 3199B Slough

Chandler Hammock 2 1 09-2074 Lake Okeechobee CTP Complex Okeechobee 3199B Slough

Chandler Hammock 3 1 13-0236 Lake Okeechobee CTP Complex Okeechobee 3199B Slough

Chandler Hammock 4 1 19-0502 Lake Okeechobee CTP Complex Okeechobee 3199B Slough

Chandler Hammock 4 1 19-0503 Lake Okeechobee CTP Complex Okeechobee 3199B Slough

Fisheating Creek 3 4 17-0292 Fisheating Creek Highlands 3201G Joe Slough Planning Unit

Fisheating Creek 3 4 17-0293 Fisheating Creek Highlands 3201G Joe Slough Planning Unit Fisheating Creek 3 4 17-0294 Fisheating Creek Highlands 3201I Platt Branch Planning Unit

Fisheating Creek 3 4 17-0295 Fisheating Creek Highlands 3201I Platt Branch Planning Unit

2 1 09-2079 Lake Okeechobee NHLMS Complex Okeechobee 3203A Nubbin Slough

2 1 09-2080 Lake Okeechobee NHLMS Complex Okeechobee 3203A Nubbin Slough

4 1 19-0504 Lake Okeechobee NHLMS Complex Okeechobee 3203B Mosquito Creek

2 1 09-2095 Lake Okeechobee TOL Complex Okeechobee 3203C L63 Canal

2 1 09-2096 Lake Okeechobee TOL Complex Okeechobee 3203C L63 Canal

Northwest Lake 1 4 06-0676 Fisheating Creek Okeechobee Glades, Highlands 3204 Harney Pond Canal Planning Unit

Northwest Lake 3 4 17-0296 Fisheating Creek Okeechobee Glades, Highlands 3204 Harney Pond Canal Planning Unit

Northwest Lake 3 4 17-0297 Fisheating Creek Okeechobee Glades, Highlands 3204 Harney Pond Canal Planning Unit Northwest Lake 3 4 17-0298 Fisheating Creek Okeechobee Glades, Highlands 3204 Harney Pond Canal Planning Unit

Taylor Creek (Lower 4 1 19-0505 Lake Okeechobee TOL Complex Okeechobee 3205B Segment)

Taylor Creek (Lower 4 1 19-0506 Lake Okeechobee TOL Complex Okeechobee 3205B Segment)

Taylor Creek (Lower 4 1 19-0507 Lake Okeechobee TOL Complex Okeechobee 3205B Segment)

Taylor Creek (Lower 4 1 19-0508 Lake Okeechobee TOL Complex Okeechobee 3205B Segment)

Taylor Creek (Lower 4 1 19-0509 Lake Okeechobee TOL Complex Okeechobee 3205B Segment)

Taylor Creek (Lower 4 1 19-0510 Lake Okeechobee TOL Complex Okeechobee 3205B Segment)

2 1 09-2076 Lake Okeechobee CTP Complex Okeechobee 3205C Popash Slough

3 1 13-0238 Lake Okeechobee CTP Complex Okeechobee 3205C Popash Slough 2 1 09-2100 Lake Okeechobee TOL Complex Okeechobee 3205D Otter Creek

4 1 19-0511 Lake Okeechobee TOL Complex Okeechobee 3205D Otter Creek

Northwest Lake 1 4 06-0677 Fisheating Creek Okeechobee Glades, Highlands 3206 Indian Prairie Canal Planning Unit

Northwest Lake 3 4 17-0299 Fisheating Creek Okeechobee Glades, Highlands 3206 Indian Prairie Canal Planning Unit

Northwest Lake 3 4 17-0300 Fisheating Creek Okeechobee Glades, Highlands 3206 Indian Prairie Canal Planning Unit

Lower Kissimmee 1 4 06-0521 Kissimmee River Okeechobee 3207 S-154C Planning Unit

Lower Kissimmee 3 4 17-0412 Kissimmee River Okeechobee 3207 S-154C Planning Unit

St. Lucie - 3 2 15-0817 Coastal Martin 3208A ICWW (Martin County) Loxahatchee

St. Lucie - ICWW (Martin County) 4 2 20-0378 Coastal Martin 3208A1 Loxahatchee above Peck Lake

St. Lucie - 4 2 20-0379 Coastal Martin 3208C Manatee Pocket Loxahatchee

St. Lucie - 4 2 20-0380 Coastal Martin 3208C Manatee Pocket Loxahatchee

St. Lucie - South St. Lucie - 1 2 03-2672 Martin 3210 Tidal St.Lucie Loxahatchee Indian River Lagoon

St. Lucie - South St. Lucie - 1 2 04-0806 Martin 3210A St. Lucie Canal Loxahatchee Indian River Lagoon St. Lucie - South St. Lucie - 4 2 20-0381 Martin 3210A St Lucie Canal Loxahatchee Indian River Lagoon

St. Lucie - South St. Lucie - South Fork St Lucie River 4 2 20-0382 Martin 3210C Loxahatchee Indian River Lagoon (Tidal Segment)

St. Lucie - South St. Lucie - 4 2 20-0383 Martin 3210E Roebuck Creek Loxahatchee Indian River Lagoon

St. Lucie - South St. Lucie - 1 2 04-0847 Martin 3211 Bessey Creek Loxahatchee Indian River Lagoon

St. Lucie - South St. Lucie - 4 2 20-0384 Martin 3211 Bessey Creek Loxahatchee Indian River Lagoon

Glades, 2 1 10-0616 Lake Okeechobee Lake Okeechobee 3212A Lake Okeechobee Okeechobee

Glades, Martin, 2 1 10-0618 Lake Okeechobee Lake Okeechobee Okeechobee, Palm 3212D Lake Okeechobee Beach

Martin, 2 1 10-0619 Lake Okeechobee Lake Okeechobee Okeechobee, Palm 3212E Lake Okeechobee Beach

Glades, Hendry, 2 1 10-0620 Lake Okeechobee Lake Okeechobee 3212F Lake Okeechobee Palm Beach

3 1 13-0239 Lake Okeechobee Lake Okeechobee Palm Beach 3212G Lake Okeechobee

2 1 10-0621 Lake Okeechobee Lake Okeechobee Hendry, Palm Beach 3212H Lake Okeechobee

2 1 09-2084 Lake Okeechobee NHLMS Complex Martin, Okeechobee 3213A Lettuce Creek

3 1 13-0240 Lake Okeechobee NHLMS Complex Martin, Okeechobee 3213A Lettuce Creek Okeechobee, St. 2 1 09-2086 Lake Okeechobee NHLMS Complex 3213B Henry Creek Lucie

Okeechobee, St. 3 1 13-0241 Lake Okeechobee NHLMS Complex 3213B Henry Creek Lucie

Okeechobee, St. 3 1 13-0242 Lake Okeechobee NHLMS Complex 3213B Henry Creek Lucie

2 1 09-2090 Lake Okeechobee NHLMS Complex Martin, St. Lucie 3213D Myrtle Slough

2 1 09-2091 Lake Okeechobee NHLMS Complex Martin, St. Lucie 3213D Myrtle Slough

3 1 13-0243 Lake Okeechobee NHLMS Complex Martin, St. Lucie 3213D Myrtle Slough

St. Lucie - South St. Lucie - 3 2 15-0818 Martin 3215 Danforth Creek Loxahatchee Indian River Lagoon

2 1 09-2092 Lake Okeechobee NHLMS Complex Martin 3219 S-153

Northwest Lake 3 4 17-0301 Fisheating Creek Okeechobee Glades 3222 L-49 Planning Unit

St. Lucie - 4 2 20-0385 Coastal Martin,Palm Beach 3226B ICWW (Martin County) Loxahatchee

Lake Worth Lagoon Lake Worth Lagoon 3 3 16-0534 - Palm Beach Intracoastal Palm Beach 3226E1 (Northern Segment) Coast Lake Worth Lagoon Lake Worth Lagoon 3 3 16-0535 - Palm Beach Intracoastal Palm Beach 3226E1 (Northern Segment) Coast

Lake Worth Lagoon Intracoastal 2 3 10-0084 - Palm Beach Palm Beach 3226EB Phil Foster Waterway Coast

Lake Worth Lagoon Lake Worth Lagoon 3 3 16-0536 - Palm Beach Intracoastal Palm Beach 3226F1 (Central Segment) Coast Lake Worth Lagoon Lake Worth Lagoon 3 3 16-0537 - Palm Beach Intracoastal Palm Beach 3226F1 (Central Segment) Coast

Lake Worth Lagoon Lake Worth Lagoon 3 3 16-0538 - Palm Beach Intracoastal Palm Beach 3226F1 (Central Segment) Coast

Lake Worth Lagoon Intracoastal 1 3 05-1170 - Palm Beach Palm Beach 3226F2 ICWW Above Pompano Waterway Coast

Lake Worth Lagoon ICWW (Palm Beach 3 3 16-0539 - Palm Beach Intracoastal Palm Beach 3226F3 County) Coast

Lake Worth Lagoon North Broward County 3 3 16-0540 - Palm Beach Intracoastal Broward 3226F4 ICWW Coast

Southeast Coast - ICWW (Broward County 2 4 10-2834 Broward 3226G1 Biscayne Bay Intracoastal Northern Segment)

Southeast Coast - Biscayne Bay ICWW (Broward County 2 4 10-2835 Broward 3226G2 Biscayne Bay Intracoastal Central Segment)

Southeast Coast - Biscayne Bay Broward, - ICWW (Broward County 2 4 10-2836 3226G3 Biscayne Bay Intracoastal Dade Southern Segment) Southeast Coast - Biscayne Bay ICWW (Miami-Dade 3 4 17-0426 Miami-Dade 3226H Biscayne Bay Intracoastal County)

Southeast Coast - Biscayne Bay ICWW (Miami-Dade 3 4 17-0427 Miami-Dade 3226H1 Biscayne Bay Intracoastal County Northern Segment)

Southeast Coast - Biscayne Bay ICWW (Miami-Dade 3 4 17-0428 Miami-Dade 3226H1 Biscayne Bay Intracoastal County Northern Segment)

Southeast Coast - Biscayne Bay 3 4 17-0429 Miami-Dade 3226H3 Port of Miami Biscayne Bay Intracoastal

Southeast Coast - Biscayne Bay (Upper 2 4 10-2837 Miami-Dade 3226L Biscayne Bay Intracoastal Segment) Southeast Coast - 1 4 06-0649 North Dade County Miami-Dade 3226M2 Upper Arch Creek Biscayne Bay Lake Worth Lagoon ICWW above Royal Palm 3 3 16-0541 - Palm Beach Intracoastal Palm Beach 3226W1 Bridge Coast

Lake Worth Lagoon 2 3 10-0090 - Palm Beach L-8 Palm Beach 3233A L-8 Coast Lake Worth Lagoon 3 3 16-0542 - Palm Beach L-8 Palm Beach 3233A L-8 Coast West 2 3 10-0427 Caloosahatchee Charlotte, Lee 3235C Cypress Creek Caloosahatchee West Charlotte, Glades, 2 3 10-0428 Caloosahatchee 3235D Jacks Branch Caloosahatchee Hendry West 2 3 10-0429 Caloosahatchee Glades, Hendry 3235E Bee Branch Caloosahatchee West 2 3 10-0431 Caloosahatchee Glades, Hendry 3235F Pollywog Creek Caloosahatchee West 2 3 10-0433 Caloosahatchee Glades 3235G Cypress Branch Caloosahatchee

West 3 3 16-0455 Caloosahatchee Glades 3235G Cypress Branch Caloosahatchee

West 3 3 16-0456 Caloosahatchee Hendry, Lee 3235I Bedman Creek Caloosahatchee

West 3 3 16-0457 Caloosahatchee Hendry 3235K1 Fort Simmons Branch Caloosahatchee

West 2 3 10-0434 Caloosahatchee Collier, Hendry 3235L Townsend Canal Caloosahatchee

West 3 3 16-0458 Caloosahatchee Collier, Hendry 3235L Townsend Canal Caloosahatchee

West 3 3 16-0459 Caloosahatchee Collier, Hendry 3235L Townsend Canal Caloosahatchee

West 3 3 16-0460 Caloosahatchee Hendry 3235M Goodno Canal Caloosahatchee

West 3 3 16-0461 Caloosahatchee Lee 3235P Olga Creek Caloosahatchee

3 3 16-0462 Caloosahatchee Telegraph Swamp Charlotte 3236 Telegraph Swamp

2 3 10-0425 Caloosahatchee Telegraph Swamp Charlotte, Lee 3236A Telegraph Creek

East 1 3 05-1115 Caloosahatchee Glades, Hendry 3237B Long Hammock Creek Caloosahatchee East 3 3 16-0463 Caloosahatchee Glades, Hendry 3237B Long Hammock Creek Caloosahatchee

East 2 3 10-0419 Caloosahatchee Glades 3237C Lake Hicpochee Caloosahatchee East 2 3 10-0420 Caloosahatchee Glades 3237C Lake Hicpochee Caloosahatchee

East 2 3 10-0421 Caloosahatchee Hendry 3237D Ninemile Canal Caloosahatchee

East 2 3 10-0422 Caloosahatchee Hendry 3237D Ninemile Canal Caloosahatchee

East 3 3 16-0464 Caloosahatchee Hendry 3237D Ninemile Canal Caloosahatchee

East 3 3 16-0465 Caloosahatchee Glades 3237E C-19 Canal Caloosahatchee

East 3 3 16-0466 Caloosahatchee Glades 3237E C-19 Canal Caloosahatchee

East 3 3 16-0467 Caloosahatchee Glades 3237E C-19 Canal Caloosahatchee

Everglades 1 5 09-0988 Palm Beach 3238 West Palm Beach Canal Agricultural Area

Everglades 1 5 09-0990 Everglades Palm Beach 3238 West Palm Beach Canal Agricultural Area Everglades 1 5 09-0993 Everglades Palm Beach 3238E M Canal Agricultural Area

Caloosahatchee 3 3 16-0468 Caloosahatchee Lee 3240A2 Cape Coral Estuary

Caloosahatchee 1 3 05-1087 Caloosahatchee Lee 3240B Tidal Caloosahatchee Estuary

Caloosahatchee Caloosahatchee Estuary 3 3 16-0469 Caloosahatchee Lee 3240B Estuary (Tidal Segment2)

Caloosahatchee Chapel Creek / Bayshore 2 3 10-0413 Caloosahatchee Lee 3240B1 Estuary Creek Caloosahatchee 1 3 05-1090 Caloosahatchee Lee 3240C Tidal Caloosahatchee Estuary

Caloosahatchee Caloosahatchee Estuary 3 3 16-0470 Caloosahatchee Lee 3240C Estuary (Tidal Segment3)

Caloosahatchee 2 3 10-0415 Caloosahatchee Lee 3240C1 Palm Creek Estuary Caloosahatchee 1 3 05-1093 Caloosahatchee Lee 3240E Yellow Fever Creek Estuary Caloosahatchee 1 3 05-1095 Caloosahatchee Lee 3240E1 Hancock Creek Estuary Caloosahatchee 1 3 05-1097 Caloosahatchee Charlotte, Lee 3240F Daughtrey Creek Estuary Caloosahatchee Whisky Creek (Wyoua 1 3 05-1100 Caloosahatchee Lee 3240H Estuary Creek)

1 3 05-1122 Caloosahatchee Lee 3240J Billy Creek

3 3 16-0471 Caloosahatchee Orange River Lee 3240J Billy Creek

Caloosahatchee 1 3 05-1106 Caloosahatchee Charlotte, Lee 3240L Gilchrest Drain--Powel Estuary Caloosahatchee 1 3 05-1108 Caloosahatchee Charlotte, Lee 3240M Stroud Creek Estuary Caloosahatchee 1 3 05-1110 Caloosahatchee Charlotte, Lee 3240N Owl Creek Estuary Caloosahatchee 1 3 05-1112 Caloosahatchee Charlotte, Lee 3240Q Popash Creek Estuary

Caloosahatchee 3 3 16-0472 Caloosahatchee Lee 3240U Winkler Canal Estuary

Caloosahatchee 3 3 16-0473 Caloosahatchee Lee 3240V Manuel Branch Estuary

Caloosahatchee 3 3 16-0474 Caloosahatchee Lee 3240W Carrell Canal Estuary

Lake Worth Lagoon Palm Beach Stations / D- 1 3 05-1164 - Palm Beach C-17 Palm Beach 3242A Canals Coast

Everglades 1 5 09-0995 Everglades Palm Beach 3244 East Beach Agricultural Area Everglades 1 5 09-0997 Everglades Palm Beach 3244 East Beach Agricultural Area

Everglades 2 5 12-0376 Everglades Palm Beach 3244 East Beach Agricultural Area

Lake Worth Lagoon 2 3 10-0069 - Palm Beach C-51 Palm Beach 3245B Lake Clarke Coast

Lake Worth Lagoon 3 3 16-0543 - Palm Beach C-51 Palm Beach 3245C1 Lake Mangonia Coast

Lake Worth Lagoon 2 3 10-0072 - Palm Beach C-51 Palm Beach 3245C4 Pine Lake Coast

Lake Worth Lagoon 3 3 16-0544 - Palm Beach C-51 Palm Beach 3245C4 Pine Lake Coast

East 2 3 12-0590 Caloosahatchee Glades, Hendry 3246 S-4 Basin Caloosahatchee

East 2 3 10-0418 Caloosahatchee Glades, Hendry 3246 S-4 Basin Caloosahatchee

East 3 3 16-0475 Caloosahatchee Glades, Hendry 3246 S-4 Basin Caloosahatchee

East 3 3 16-0476 Caloosahatchee Glades, Hendry 3246 S-4 Basin Caloosahatchee

Everglades 1 5 09-1001 Everglades Palm Beach 3247 715 Farms Agricultural Area Everglades 2 5 12-0377 Everglades Palm Beach 3247 715 Farms Agricultural Area

Everglades 1 5 09-1004 Everglades Palm Beach 3248 N. New River Canal Agricultural Area

Everglades 1 5 09-1006 Everglades Palm Beach 3248A Agricultural Area

Everglades 1 5 09-1008 Everglades Hendry, Palm Beach 3250 S-236 Agricultural Area

Water Conservation 1 5 09-1027 Everglades Palm Beach 3252 WCA1 Center Sector Area 1

Water Conservation 1 5 09-1028 Everglades Palm Beach 3252B WCA 1 (North Sector) Area 1

Everglades 1 5 09-1012 Everglades Palm Beach 3253 South Bay Agricultural Area

Everglades 1 5 09-1014 Everglades Palm Beach 3254 Hillsboro Canal Agricultural Area

Lake Worth Lagoon 3 3 16-0545 - Palm Beach C-16 Palm Beach 3256A Lake Osborne Coast

Lake Worth Lagoon 3 3 16-0546 - Palm Beach C-16 Palm Beach 3256A Lake Osborne Coast Lake Worth Lagoon 3 3 16-0547 - Palm Beach C-16 Palm Beach 3256A Lake Osborne Coast

Everglades West 4 1 19-0462 Estero Bay Lee 3258A1 Estero Bay Wetlands Coast

Everglades West 3 1 13-0244 Estero Bay Lee 3258B2 Hendry Creek Coast

Everglades West 4 1 19-0463 Estero Bay Lee 3258B2 Hendry Creek Coast

Everglades West 4 1 19-0464 Estero Bay Lee 3258C2 Mullock Creek Coast

Everglades West 4 1 19-0465 Estero Bay Lee 3258C2 Mullock Creek Coast

Everglades West Mullock Creek (Marine 3 1 13-0247 Estero Bay Lee 3258C4 Coast Segment)

Everglades West Mullock Creek (Marine 4 1 19-0466 Estero Bay Lee 3258C4 Coast Segment)

Everglades West 4 1 19-0467 Estero Bay Lee 3258C5 Ten Mile Canal South Coast

Everglades West (Marine 3 1 13-0249 Estero Bay Lee 3258D1 Coast Segment)

Everglades West Estero River (Marine 4 1 19-0468 Estero Bay Lee 3258D1 Coast Segment)

Everglades West Estero River (Marine 4 1 19-0469 Estero Bay Lee 3258D1 Coast Segment) Everglades West 4 1 19-0470 Estero Bay Lee 3258EA Coast

Everglades West Imperial River (Marine 3 1 13-0253 Estero Bay Lee 3258EB Coast Segment)

Everglades West Imperial River (Marine 4 1 19-0471 Estero Bay Lee 3258EB Coast Segment)

Everglades West Imperial River (Marine 4 1 19-0472 Estero Bay Lee 3258EB Coast Segment)

Everglades West Imperial River (Marine 4 1 19-0473 Estero Bay Lee 3258EB Coast Segment)

Everglades West Imperial River (Marine 4 1 19-0474 Estero Bay Lee 3258EB Coast Segment)

Everglades West 3 1 13-0254 Estero Bay Collier, Lee 3258F Oak Creek Coast

Everglades West Spring Creek (Marine 3 1 13-0255 Estero Bay Lee 3258H2 Coast Segment)

Everglades West Spring Creek (Marine 3 1 13-0257 Estero Bay Lee 3258H2 Coast Segment)

Everglades West Spring Creek (Marine 4 1 19-0475 Estero Bay Lee 3258H2 Coast Segment)

Everglades West Spring Creek (Marine 4 1 19-0476 Estero Bay Lee 3258H2 Coast Segment) Everglades West Spring Creek (Marine 4 1 19-0477 Estero Bay Lee 3258H2 Coast Segment)

Everglades West 4 1 19-0478 Estero Bay Lee 3258I Estero Bay Coast

Everglades West 4 1 19-0479 Southwest Coast Collier, Lee 3259A Cocohatchee River Coast

Everglades West 4 1 19-0480 Southwest Coast Collier, Lee 3259A Cocohatchee River Coast Everglades West Drainage to Corkscrew 3 1 13-0258 Southwest Coast Collier, Lee 3259B1 Coast Swamp

Everglades West 3 1 13-0260 Southwest Coast Collier, Monroe 3259M Ten Thousand Islands Coast

Everglades West 4 1 19-0481 Southwest Coast Collier, Monroe 3259M Ten Thousand Islands Coast

Everglades 2 5 12-0380 Everglades Hendry, Palm Beach 3260 S-8 Agricultural Area

Lake Worth Lagoon 2 3 10-0057 - Palm Beach C-15 Palm Beach 3262 E-4 Canal Coast

Lake Worth Lagoon 3 3 16-0548 - Palm Beach C-15 Palm Beach 3262A Lake Ida Coast

Lake Worth Lagoon 3 3 16-0549 - Palm Beach C-15 Palm Beach 3262A Lake Ida Coast

Lake Worth Lagoon 3 3 16-0550 - Palm Beach C-15 Palm Beach 3262A Lake Ida Coast

Lake Worth Lagoon 3 3 16-0551 - Palm Beach C-15 Palm Beach 3262B1 E-1 Canal Coast Lake Worth Lagoon 2 3 10-0059 - Palm Beach C-15 Palm Beach 3262D E-3 Canal Coast

Lake Worth Lagoon 2 3 10-0081 - Palm Beach Hillsboro Canal Palm Beach 3264A E-1 Canal Coast

Lake Worth Lagoon 1 3 05-1168 - Palm Beach Hillsboro Canal Palm Beach 3264D E-4 Canal Coast

Lake Worth Lagoon 2 3 10-0082 - Palm Beach Hillsboro Canal Palm Beach 3264D E-4 Canal Coast

Water Conservation Broward, Palm 1 5 09-1030 Everglades 3265H WCA2A Center Sector Area 2 Beach

Southeast Coast - 2 4 10-2841 Broward County Broward 3271 Pompano Canal Biscayne Bay

Southeast Coast - 1 4 06-0632 Broward County Broward 3276A North Fork New River Biscayne Bay

Southeast Coast - 3 4 17-0430 Broward County Broward 3276A New River (North Fork) Biscayne Bay

Southeast Coast - 2 4 10-2846 Broward County Broward 3277A New River Canal (South) Biscayne Bay

Everglades West 4 1 19-0482 Southwest Coast Collier 3278C Wiggins Bay Outlet Coast

Everglades West 4 1 19-0483 Southwest Coast Collier 3278K Gordon River Extension Coast

Everglades West 4 1 19-0484 Southwest Coast Collier 3278O Marco Island Coast

Everglades West Marco Island (South 4 1 19-0485 Southwest Coast Collier 3278P Coast Segment)

Everglades West Marco Island (South 4 1 19-0486 Southwest Coast Collier 3278P Coast Segment) Everglades West Marco Island (South 4 1 19-0487 Southwest Coast Collier 3278P Coast Segment)

Everglades West 3 1 13-0263 Southwest Coast Collier 3278Q1 Clam Bay Coast

Everglades West 4 1 19-0488 Southwest Coast Collier 3278Q2 Moorings Bay System Coast

Everglades West 3 1 13-0264 Southwest Coast Collier 3278R1 Haldeman Creek (Lower) Coast

Everglades West 4 1 19-0489 Southwest Coast Collier 3278R1 Haldeman Creek (Lower) Coast

Everglades West 3 1 13-0266 Southwest Coast Collier 3278R3 Rock Creek Coast

Everglades West 3 1 13-0267 Southwest Coast Collier 3278R3 Rock Creek Coast

Everglades West 4 1 19-0490 Southwest Coast Collier 3278R3 Rock Creek Coast

Everglades West Naples Bay (Coastal 3 1 13-0268 Southwest Coast Collier 3278R4 Coast Segment)

Everglades West Naples Bay (Coastal 3 1 13-0269 Southwest Coast Collier 3278R4 Coast Segment)

Everglades West Naples Bay (Coastal 4 1 19-0491 Southwest Coast Collier 3278R4 Coast Segment)

Everglades West Naples Bay (Coastal 4 1 19-0492 Southwest Coast Collier 3278R4 Coast Segment)

Everglades West Naples Bay (Coastal 4 1 19-0493 Southwest Coast Collier 3278R4 Coast Segment) Everglades West Gordon River (Marine 3 1 13-0270 Southwest Coast Collier 3278R5 Coast Segment)

Everglades West Gordon River (Marine 3 1 13-0271 Southwest Coast Collier 3278R5 Coast Segment)

Everglades West Gordon River (Marine 4 1 19-0494 Southwest Coast Collier 3278R5 Coast Segment)

Everglades West Gordon River (Marine 4 1 19-0495 Southwest Coast Collier 3278R5 Coast Segment)

Everglades West Gordon River (Marine 4 1 19-0496 Southwest Coast Collier 3278R5 Coast Segment)

Everglades West Gordon River (Marine 4 1 19-0497 Southwest Coast Collier 3278R5 Coast Segment)

Everglades West Gordon River (Marine 4 1 19-0498 Southwest Coast Collier 3278R5 Coast Segment)

Everglades West 2 1 09-2714 Southwest Coast Collier 3278S North Golden Gate Coast

Everglades West 2 1 09-2717 Southwest Coast Collier 3278U Rookery Bay Coastal Coast Everglades West 4 1 19-0499 Interdrainage Area Collier 3278W Silver Strand Coast

Southeast Coast - 2 4 10-2854 Broward County Broward 3282 C-10 (Hollywood Canal) Biscayne Bay Southeast Coast - Broward, Miami- 1 4 06-0637 North Dade County 3283 Snake Creek Canal East Biscayne Bay Dade

Southeast Coast - 3 4 17-0431 North Dade County Miami-Dade 3286C C-5/Comfort Canal Biscayne Bay

Southeast Coast - 1 4 06-0643 North Dade County Miami-Dade 3288 C-6/ Biscayne Bay Southeast Coast - 2 4 10-2858 North Dade County Miami-Dade 3288A Wagner Creek Biscayne Bay

Southeast Coast - 2 4 12-0610 North Dade County Miami-Dade 3288A Wagner Creek Biscayne Bay

Southeast Coast - 1 4 06-0647 North Dade County Miami-Dade 3292 Coral Gables Canal Biscayne Bay Southeast Coast - 2 4 10-2864 North Dade County Miami-Dade 3293 C-2/ Biscayne Bay Southeast Coast - 2 4 10-2867 South Dade County Miami-Dade 3295 C-100 Biscayne Bay

Southeast Coast - 3 4 17-0432 South Dade County Miami-Dade 3298A Goulds Canal Biscayne Bay

Southeast Coast - 3 4 17-0433 South Dade County Miami-Dade 3302 C-103 (Mowry Canal) Biscayne Bay

Southeast Coast - 3 4 17-0434 South Dade County Miami-Dade 3304 Military Canal Biscayne Bay

2 1 09-1917 Suwannee Withlacoochee River Hamilton 3321 Lake Octahatchee Outlet 4 1 19-0577 Suwannee Withlacoochee River Madison 3322A Lake Cherry

Suwannee River (Upper 4 1 19-0578 Suwannee Upper Suwannee Columbia, Hamilton 3341B Segment)

4 1 19-0579 Suwannee Withlacoochee River Hamilton, Suwannee 3341X Rise

2 1 09-1922 Suwannee Withlacoochee River Madison 3366 Lake Francis Outlet

4 1 19-0580 Suwannee Withlacoochee River Madison 3366A Lake Francis

4 1 19-0581 Suwannee Withlacoochee River Madison 3366A Lake Francis

Choctawhatchee - Choctawhatchee 3 3 16-0491 Washington 337 Flat Creek St. Andrew River

4 1 19-0582 Suwannee Upper Suwannee Hamilton 3389 Sugar Creek

2 1 09-1804 Suwannee Econfina Madison, Taylor 3402

2 1 09-1817 Suwannee Lower Suwannee Dixie, Levy 3422D Lower Suwannee Estuary

Gulf of Mexico (Levy And 3 1 13-0116 Suwannee Lower Suwannee Dixie, Levy 3422D Dixie County; )

Gulf of Mexico (Levy And 4 1 19-0583 Suwannee Lower Suwannee Dixie, Levy 3422D Dixie County; Suwannee River) Suwannee River 4 1 19-0584 Suwannee Lower Suwannee Dixie, Levy 3422G (Estuarine Segment)

Suwannee River 4 1 19-0585 Suwannee Lower Suwannee Dixie, Levy 3422G (Estuarine Segment)

Suwannee River 4 1 19-0586 Suwannee Lower Suwannee Dixie, Levy 3422G (Estuarine Segment)

Suwannee River 4 1 19-0587 Suwannee Lower Suwannee Dixie, Levy 3422G (Estuarine Segment)

Fenholloway River Below 2 1 09-1811 Suwannee Fenholloway Taylor 3473B Pulp Mill

Fenholloway River Below 2 1 09-1810 Suwannee Fenholloway Taylor 3473B Pulp Mill

Fenholloway River below 4 1 19-0588 Suwannee Fenholloway Taylor 3473B Buckeye Pulp Mill

Choctawhatchee - Choctawhatchee Cypress Springs 3 3 16-0492 Washington 348Z St. Andrew River (Washington County)

2 1 09-1842 Suwannee Middle Suwannee Suwannee 3496A Low Lake

1 4 06-0619 Pensacola Yellow River Okaloosa, Walton 35 Pond Creek

Choctawhatchee - Choctawhatchee 3 3 16-0493 Walton 351 Alaqua Creek St. Andrew Bay

2 1 09-1815 Suwannee Fenholloway Taylor 3518 Spring Creek 3 1 13-0120 Suwannee Columbia 3531 Rose Creek

2 1 09-1847 Suwannee Other Coastal Taylor 3556 Weaver Warrior Creek

2 1 09-1890 Suwannee Steinhatchee Lafayette 3573B 2 1 09-1887 Suwannee Steinhatchee Taylor 3603 Bevins (Boggy) Creek

2 1 09-1884 Suwannee Santa Fe River Alachua, Bradford 3605F Altho Drainage

4 1 19-0589 Suwannee Santa Fe River Alachua 3626 Pareners Branch

4 1 19-0590 Suwannee Santa Fe River Alachua 3644 Mill Creek Sink

4 1 19-0591 Suwannee Santa Fe River Alachua 3678A Cellon Creek

4 1 19-0592 Suwannee Santa Fe River Alachua 3682 Blues Creek

4 1 19-0593 Suwannee Santa Fe River Alachua 3682 Blues Creek

4 1 19-0594 Suwannee Waccasassa River Gilchrist, Levy 3699 Waccasassa River 4 1 19-0595 Suwannee Waccasassa River Levy 3699A Waccasassa River

3 1 13-0125 Suwannee Waccasassa River Levy 3699B Waccasassa River

3 1 15-1539 Suwannee Waccasassa River Levy 3699B Waccasassa River

4 1 19-0596 Suwannee Waccasassa River Levy 3699B Waccasassa River

4 1 19-0597 Suwannee Waccasassa River Levy 3699B Waccasassa River

4 1 19-0598 Suwannee Waccasassa River Levy 3703B Blue Spring (Levy County)

4 1 19-0599 Suwannee Other Coastal Dixie 3705 Butler Creek (Lilly Creek)

4 1 19-0600 Suwannee Other Coastal Dixie 3721 Direct Runoff To Gulf

3 1 13-0127 Suwannee Other Coastal Dixie 3724 Direct Runoff to Gulf

3 1 13-0128 Suwannee Other Coastal Dixie 3724 Direct Runoff to Gulf

4 1 19-0601 Suwannee Other Coastal Dixie 3724 Direct Runoff To Gulf

3 1 13-0129 Suwannee Other Coastal Dixie 3725 Direct Runoff to Gulf

3 1 13-0130 Suwannee Waccasassa River Levy 3729A Black Point Swamp 3 1 13-0131 Suwannee Waccasassa River Levy 3729A Black Point Swamp

2 1 09-1915 Suwannee Waccasassa River Levy 3731A Lake Marion

Apalachicola - 4 2 20-0246 Apalachicola River Gulf, Franklin 375C Apalachicola River Chipola

Apalachicola - 4 2 20-0247 Apalachicola River Gulf,Franklin 375C Apalachicola River Chipola

Apalachicola - 3 2 18-0805 Apalachicola River Gadsden 376A Mosquito Creek Chipola

Apalachicola - 4 2 20-0248 Apalachicola River Gadsden 376A Mosquito Creek Chipola

Apalachicola - 4 2 20-0249 Apalachicola River Gadsden 393 South Mosquito Creek Chipola

Ochlockonee - St. North Ochlockonee 3 1 13-0078 Gadsden 424 Little River Marks River

Ochlockonee - St. North Ochlockonee 4 1 19-0534 Gadsden 424 Little River Marks River

Ochlockonee - St. 2 1 09-1948 Jefferson 459 Ward Creek Marks Ochlockonee - St. North Ochlockonee 3 1 13-0079 Gadsden 480 Salem Branch Marks River

Ochlockonee - St. North Ochlockonee 4 1 19-0535 Gadsden 480 Salem Branch Marks River

Ochlockonee - St. North Ochlockonee 4 1 19-0536 Gadsden 480 Salem Branch Marks River

Ochlockonee - St. North Ochlockonee 4 1 19-0537 Gadsden 480 Salem Branch Marks River

Apalachicola - 4 2 20-0250 Apalachicola River Gadsden 487 Flat Creek Chipola

Apalachicola - 4 2 20-0251 Apalachicola River Gadsden 488 Unnamed Branch Chipola

Choctawhatchee - Choctawhatchee 3 3 16-0494 Okaloosa 495A Turkey Creek St. Andrew Bay

Choctawhatchee - Choctawhatchee 3 3 16-0495 Walton, Washington 49B St. Andrew River

Choctawhatchee - Choctawhatchee 3 3 16-0496 Holmes 49F Choctawhatchee River St. Andrew River St. Lucie - 4 2 20-0386 Coastal Martin 5003AB Stuart Causeway Loxahatchee

St. Lucie - South Causeway at Boat 4 2 20-0387 Coastal St. Lucie 5003AD Loxahatchee Ramp

Indian River South Central Indian South Indian River (below 3 5 18-0293 Indian River 5003B1 Lagoon River Lagoon SR 60)

Indian River South Central Indian South Indian River (below 3 5 18-0294 Indian River 5003B1 Lagoon River Lagoon SR 60)

Indian River South Central Indian South Indian River (Below 2 5 13-1343 Indian River 5003B2 Lagoon River Lagoon SR 60 - Shellfish Portion)

Indian River South Central Indian South Indian River (above 3 5 18-0295 Indian River 5003C1 Lagoon River Lagoon SR 60)

Indian River South Central Indian Brevard, Indian South Indian River (Near 2 5 13-1345 5003D1 Lagoon River Lagoon River St. Sebastian River)

Apalachicola - 2 2 09-1646 Apalachicola River Calhoun, Jackson 512 Wilson Creek Chipola

Apalachicola - 4 2 20-0252 Calhoun 51B Chipola River Chipola

Apalachicola - 4 2 20-0253 Chipola River Calhoun 51B Chipola River Chipola Apalachicola - 3 2 18-0806 Chipola River Jackson 51E Chipola River Chipola

Apalachicola - 4 2 20-0254 Chipola River Jackson 51E Chipola River Chipola

Apalachicola - 4 2 20-0255 Chipola River Jackson 52 Cowarts Creek Chipola

3 4 17-0420 Pensacola Pensacola Bay Santa Rosa 534 Sandy Point Bayou

Choctawhatchee - Choctawhatchee 3 3 16-0497 Holmes 54 Wrights Creek St. Andrew River

Ochlockonee - St. North Ochlockonee 3 1 13-0081 Gadsden 540A Tallavanna Lake Marks River

1 5 09-0983 Perdido Perdido River Escambia 542 Rest Area Run

Ochlockonee - St. 4 1 19-0538 Leon 546C Lake Monkey Business Marks

Ochlockonee - St. 4 1 19-0539 Lake Iamonia Leon 546C Lake Monkey Business Marks

Ochlockonee - St. 4 1 19-0540 Lake Iamonia Leon 546C Lake Monkey Business Marks

Escambia, Santa Escambia Bay (North 3 4 17-0421 Pensacola Pensacola Bay 548AA Rosa Segment) Escambia, Santa Escambia Bay North 2 4 10-3051 Pensacola Pensacola Bay 548AC Rosa (Shellfish)

Escambia, Santa Escambia Bay (South 2 4 10-3053 Pensacola Pensacola Bay 548B Rosa Segment)

Escambia, Santa Pensacola Bay (North 2 4 10-3055 Pensacola Pensacola Bay 548C Rosa Segment)

Escambia, Santa Pensacola Bay (Middle 3 4 17-0422 Pensacola Pensacola Bay 548D Rosa Segment)

1 4 06-0598 Pensacola Pensacola Bay Escambia 548FB Navy Point

Blackwater Bay (South 2 4 10-3058 Pensacola Pensacola Bay Santa Rosa 548GB Segment)

Blackwater Bay (South 2 4 10-3059 Pensacola Pensacola Bay Santa Rosa 548GB Segment)

2 4 10-3061 Pensacola Pensacola Bay Santa Rosa 548H East Bay

Ochlockonee - St. 4 1 19-0541 Lake Iamonia Leon 564A Lake Arrowhead Marks

Ochlockonee - St. 4 1 19-0542 Lake Iamonia Leon 564A Lake Arrowhead Marks Ochlockonee - St. 4 1 19-0543 Lake Iamonia Leon 564C Petty Gulf Lake Marks

Ochlockonee - St. 4 1 19-0544 Lake Iamonia Leon 564C Petty Gulf Lake Marks

Ochlockonee - St. 4 1 19-0545 Lake Iamonia Leon 564C Petty Gulf Lake Marks

Ochlockonee - St. 4 1 19-0546 Lake Iamonia Leon 564C Petty Gulf Lake Marks

Apalachicola - 2 2 09-1673 Chipola River Calhoun, Jackson 569 Tenmile Creek Chipola Apalachicola - 2 2 09-1671 Chipola River Jackson 57 Jordan Bay Drain Chipola

Ochlockonee - St. 3 1 13-0083 Lake Jackson Leon 582D Lake Jackson Outlet Marks

Ochlockonee - St. North Ochlockonee 4 1 19-0547 Gadsden 595 Tanyard Branch Marks River Ochlockonee - St. North Ochlockonee 4 1 19-0548 Gadsden 595 Tanyard Branch Marks River

Ochlockonee - St. North Ochlockonee 4 1 19-0549 Gadsden 595 Tanyard Branch Marks River

Ochlockonee - St. North Ochlockonee 4 1 19-0550 Gadsden 595 Tanyard Branch Marks River

Choctawhatchee - Choctawhatchee Holmes Creek (Lower 3 3 16-0498 Washington 59D St. Andrew River Segment)

Southeast Coast - Biscayne Bay 3 4 17-0435 Miami-Dade 6001 Biscayne Bay Biscayne Bay Intracoastal

1 5 09-0961 Florida Keys Upper Keys Monroe 6006A South Key Largo

1 5 09-0962 Florida Keys Upper Keys Monroe 6006C North Key Largo

1 5 09-0963 Florida Keys Upper Keys Monroe 6009 Plantation Key 1 5 09-0957 Florida Keys Middle Keys Monroe 6011A Vaca Key 1 5 09-0944 Florida Keys Lower Keys Monroe 6012A Big Pine Key 1 5 09-0945 Florida Keys Lower Keys Monroe 6013C Cudjoe Key 1 5 09-0947 Florida Keys Lower Keys Monroe 6014A Key West 1 5 09-0948 Florida Keys Lower Keys Monroe 6014B Stock Island 2 5 12-0436 Florida Keys Upper Keys Monroe 6017 Upper Matecumbe Key

1 5 09-0964 Florida Keys Upper Keys Monroe 6019 Lower Matecumbe Key

Ochlockonee - St. 4 1 19-0551 St. Marks River Leon 628 Black Creek Marks

2 4 10-3063 Pensacola Pensacola Bay Escambia 639 Direct Runoff to Bay

3 4 17-0423 Pensacola Pensacola Bay Escambia 639 Direct Runoff to Bay

Ochlockonee - St. 4 1 19-0552 Lake Lafayette Leon 647A Lake Tom John Marks

Ochlockonee - St. 4 1 19-0553 Lake Lafayette Leon 647A Lake Tom John Marks

Ochlockonee - St. 4 1 19-0554 Lake Lafayette Leon 647A Lake Tom John Marks

Ochlockonee - St. 4 1 19-0555 Lake Lafayette Leon 647I Shakey Pond Marks

Ochlockonee - St. 4 1 19-0556 Lake Lafayette Leon 647I Shakey Pond Marks

Choctawhatchee - Choctawhatchee 2 3 10-0474 Walton 679 Black Creek St. Andrew River Ochlockonee - St. 2 1 09-1989 Telogia Creek Gadsden, Liberty 684 Mule Creek Marks Ochlockonee - St. 2 1 09-1937 Lake Jackson Leon 689 Lake Overstreet Drain Marks

Choctawhatchee - Choctawhatchee 3 3 16-0500 Okaloosa 692 Boggy Bayou St. Andrew Bay Choctawhatchee - Choctawhatchee 3 3 16-0499 Okaloosa 692 Boggy Bayou St. Andrew Bay

Choctawhatchee - Choctawhatchee 2 3 10-0456 Okaloosa 692A Lincoln Park St. Andrew Bay

East Bay River (Marine 2 4 10-3066 Pensacola Pensacola Bay Santa Rosa 701A Portion)

East Bay River (Marine 3 4 17-0424 Pensacola Pensacola Bay Santa Rosa 701A Portion)

Choctawhatchee - Choctawhatchee 2 3 10-0437 Walton 712 Mullet Creek St. Andrew Bay

Ochlockonee - St. 4 1 19-0557 Lake Miccosukee Jefferson 716 Caney Branch Marks

Choctawhatchee - Choctawhatchee 2 3 10-0438 Okaloosa 722 Rocky Bayou St. Andrew Bay Choctawhatchee - Choctawhatchee 1 3 05-1132 Okaloosa 722B Rocky Bayou State Park St. Andrew Bay Apalachicola - 2 2 09-1647 Apalachicola River Calhoun 723 Stafford Creek Chipola

Apalachicola - 4 2 20-0256 Apalachicola River Liberty 728 Sweetwater Creek Chipola

Choctawhatchee - Choctawhatchee 3 3 16-0502 Walton 731 Alaqua Bayou St. Andrew Bay

1 4 06-0602 Pensacola Pensacola Bay Escambia 738AB Bayview Park Pier

Choctawhatchee - Choctawhatchee 2 3 10-0441 Walton 742 Basin Bayou St. Andrew Bay Ochlockonee - St. 3 1 13-0090 Lake Jackson Leon 746A Harbinwood Estates Drain Marks

Apalachicola - 2 2 09-1674 Chipola River Bay, Calhoun 749 Juniper Creek Chipola

Choctawhatchee - Choctawhatchee 3 3 16-0503 Walton 751 Eagle Creek St. Andrew Bay

Choctawhatchee - Choctawhatchee 2 3 10-0457 Okaloosa 754A Poquito Park St. Andrew Bay

Ochlockonee - St. 4 1 19-0558 Lake Lafayette Leon 756B Lake Piney Z Marks

Ochlockonee - St. 4 1 19-0559 Lake Lafayette Leon 756B Lake Piney Z Marks

Ochlockonee - St. 4 1 19-0560 Lake Lafayette Leon 756B Lake Piney Z Marks

Ochlockonee - St. 3 1 13-0093 Lake Lafayette Leon 756I Lake Lafayette Drain Marks

Ochlockonee - St. North Ochlockonee 4 1 19-0561 Gadsden 757 Bear Creek Marks River Ochlockonee - St. 4 1 19-0562 Lake Jackson Leon 758 Lexington Creek Marks

Choctawhatchee - Choctawhatchee 1 3 05-1133 Okaloosa 778A Choctawhatchee Bay St. Andrew Bay

Choctawhatchee - Choctawhatchee Choctawhatchee Bay 2 3 10-0458 Okaloosa 778A St. Andrew Bay (Lower Segment)

Choctawhatchee - Choctawhatchee Choctawhatchee Bay 3 3 16-0504 Okaloosa 778A St. Andrew Bay (Lower Segment)

Choctawhatchee - Choctawhatchee Choctawhatchee Bay 3 3 16-0505 Okaloosa 778A St. Andrew Bay (Lower Segment)

Choctawhatchee - Choctawhatchee 2 3 10-0459 Okaloosa 778AB East Pass St. Andrew Bay

Choctawhatchee - Choctawhatchee Gulf Island National 1 3 05-1131 Okaloosa 778AC St. Andrew Bay Seashore

Choctawhatchee - Choctawhatchee 3 3 16-0506 Okaloosa 778AD Clement E. Taylor Park St. Andrew Bay

Choctawhatchee - Choctawhatchee Choctawhatchee Bay 2 3 13-1333 Okaloosa 778B St. Andrew Bay (Middle Segment1) Choctawhatchee - Choctawhatchee Choctawhatchee Bay 3 3 16-0507 Okaloosa 778B St. Andrew Bay (Middle Segment1)

Choctawhatchee - Choctawhatchee Choctawhatchee Bay 3 3 16-0508 Okaloosa 778B St. Andrew Bay (Middle Segment1)

Choctawhatchee - Choctawhatchee Choctawhatchee Bay 2 3 13-1334 Okaloosa, Walton 778C St. Andrew Bay (Middle Segment2)

Choctawhatchee - Choctawhatchee Choctawhatchee Bay 3 3 16-0509 Okaloosa, Walton 778C St. Andrew Bay (Middle Segment2)

Choctawhatchee - Choctawhatchee Choctawhatchee Bay 3 3 16-0510 Okaloosa, Walton 778C St. Andrew Bay (Middle Segment2)

Choctawhatchee - Choctawhatchee 2 3 10-0461 Okaloosa, Walton 778CD Camp Timpoochee St. Andrew Bay

Choctawhatchee - Choctawhatchee Choctawhatchee Bay 3 3 16-0511 Walton 778D St. Andrew Bay (Upper Segment)

Choctawhatchee - Choctawhatchee Choctawhatchee Bay 3 3 16-0512 Walton 778D St. Andrew Bay (Upper Segment) Choctawhatchee - Choctawhatchee Choctawhatchee Bay 3 3 16-0513 Walton 778D St. Andrew Bay (Upper Segment)

Choctawhatchee - 3 3 16-0514 St. Andrews Bay Washington 780A Lake St. Andrew

Choctawhatchee - 3 3 16-0515 St. Andrews Bay Washington 780A Rattlesnake Lake St. Andrew

Choctawhatchee - Choctawhatchee 3 3 16-0516 Okaloosa 786A Bass Lake St. Andrew Bay

Choctawhatchee - Choctawhatchee 3 3 16-0517 Okaloosa 786A Bass Lake St. Andrew Bay

Ochlockonee - St. 3 1 13-0097 Lake Miccosukee Jefferson, Leon 791L Lake Miccosukee Outlet Marks

Ochlockonee - St. St Marks River (South 3 1 13-0098 St. Marks River Wakulla 793A Marks Segment)

St Marks River (Marine Ochlockonee - St. 4 1 19-0563 St. Marks River Wakulla 793A Segment below Wakulla Marks River)

Ochlockonee - St. Jefferson, Leon, St Marks River 4 1 19-0564 St. Marks River 793D Marks Wakulla (Freshwater Segment)

Perdido Bay (Upper 3 5 18-0296 Perdido Perdido Bay Escambia 797 Segment) Choctawhatchee - Choctawhatchee 3 3 16-0518 Jackson 80 Little Creek St. Andrew River

Emerald Promenade 3 4 17-0425 Pensacola Pensacola Bay Okaloosa 8007A Beachwalk (Santa Rosa Island)

Choctawhatchee - Choctawhatchee 3 3 16-0519 Okaloosa 8008B Henderson Park Beach St. Andrew Bay

Choctawhatchee - Choctawhatchee 2 3 10-0462 Okaloosa 8008C James Lee Park St. Andrew Bay

Choctawhatchee - Choctawhatchee 2 3 10-0463 Okaloosa 8008E Wayside Park St. Andrew Bay

Choctawhatchee - Choctawhatchee 3 3 16-0520 Walton 8009A Dune Allen Beach St. Andrew Bay

Choctawhatchee - Choctawhatchee 3 3 16-0521 Walton 8010A Blue Mountain Beach St. Andrew Bay

Choctawhatchee - Choctawhatchee 3 3 16-0522 Walton 8010B Grayton Beach St. Andrew Bay Choctawhatchee - Choctawhatchee 3 3 16-0523 Walton 8010C Holley Street Beach St. Andrew Bay

Choctawhatchee - 1 3 05-1155 St. Andrews Bay Bay 8012B Laguna Beach St. Andrew

Choctawhatchee - Panama City Beach, City 3 3 16-0524 St. Andrews Bay Bay 8012C St. Andrew Pier

Choctawhatchee - 1 3 05-1158 St. Andrews Bay Bay 8013B Beckrich Road St. Andrew

Choctawhatchee - 3 3 16-0525 St. Andrews Bay Bay 8015B East County Line St. Andrew

Choctawhatchee - 3 3 16-0526 St. Andrews Bay Bay, Gulf 8015C Lookout Beach St. Andrew

Choctawhatchee - 3 3 16-0527 St. Andrews Bay Gulf 8015D Beacon Hill Beach St. Andrew

Choctawhatchee - 3 3 16-0528 St. Andrews Bay Gulf 8015E St Joe Beach St. Andrew Choctawhatchee - 3 3 16-0529 St. Andrews Bay Bay 8015F St. Andrew

Apalachicola - St George Island (Franklin 4 2 20-0257 Apalachicola Bay Franklin 8021A Chipola Boulevard)

Ochlockonee - St. South Ochlockonee Gulf of Mexico (Franklin 3 1 13-0100 Franklin, Wakulla 8025 Marks River County; Ochlockonee Bay)

Ochlockonee - St. South Ochlockonee 2 1 09-1982 Wakulla 8025B Mashes Island Marks River

Ochlockonee - St. Coastal Watershed 2 1 09-1933 Wakulla 8026B Shell Point Marks and Apalachee Bay

Ochlockonee - St. Coastal Watershed Gulf of Mexico (Wakulla 4 1 19-0565 Wakulla 8026C Marks and Apalachee Bay County; Apalachee Bay)

Gulf of Mexico (Taylor 4 1 19-0602 Suwannee Other Coastal Dixie, Taylor 8033 County; Steinhatchee River)

Gulf of Mexico (Dixie 4 1 19-0603 Suwannee Other Coastal Dixie 8034A County)

Gulf of Mexico (Dixie 3 1 13-0137 Suwannee Other Coastal Dixie 8035B County-Shellfish Portion)

Gulf of Mexico (Dixie 4 1 19-0604 Suwannee Other Coastal Dixie 8035B County-Shellfish Portion)

Gulf of Mexico (Dixie 4 1 19-0605 Suwannee Other Coastal Dixie 8035B County-Shellfish Portion) Gulf of Mexico (Dixie 4 1 19-0606 Suwannee Other Coastal Dixie 8035B County-Shellfish Portion)

Gulf of Mexico (Levy 4 1 19-0607 Suwannee Waccasassa River Levy 8037D County; Cedar Key)

2 1 09-1914 Suwannee Waccasassa River Levy 8038 Waccasassariver Gulf 2

Crystal River / Kings Gulf of Mexico 3 5 18-0324 Springs Coast Citrus, Levy 8038C Bay Planning Unit (Withlacoochee River)

Crystal River / Kings Gulf of Mexico 3 5 18-0325 Springs Coast Citrus, Levy 8038C Bay Planning Unit (Withlacoochee River)

Crystal River / Kings Gulf of Mexico 3 5 18-0326 Springs Coast Citrus, Levy 8038C Bay Planning Unit (Withlacoochee River)

Crystal River / Kings Gulf of Mexico 3 5 18-0327 Springs Coast Citrus, Levy 8038C Bay Planning Unit (Withlacoochee River)

Crystal River / Kings Gulf of Mexico (Citrus 2 5 13-1348 Springs Coast Citrus, Levy 8039 Bay Planning Unit County; Crystal River)

Crystal River / Kings Gulf of Mexico (Citrus 2 5 12-0549 Springs Coast Citrus, Levy 8039 Bay Planning Unit County; Crystal River)

Homosassa River Gulf of Mexico (Citrus 2 5 13-1349 Springs Coast Citrus 8040 Planning Unit County)

Gulf of Mexico (Pasco 3 5 18-0328 Springs Coast Middle Coastal Hernando, Pasco 8043 County; Hernando County)

Gulf of Mexico (Pasco 3 5 18-0329 Springs Coast Middle Coastal Hernando, Pasco 8043 County; Hernando County) 1 5 09-1096 Springs Coast Middle Coastal Pasco 8044A Robert J Strickland Beach

Gulf of Mexico (Pasco 3 5 18-0330 Springs Coast Middle Coastal Pasco 8044E County; )

Sarasota Bay - 3 3 16-0722 Sarasota Bay Sarasota 8053D Venice Beach Peace - Myakka

Gulf of Mexico (Collier Everglades West 4 1 19-0500 Southwest Coast Collier 8063 County; Rookery Bay- Coast Naples)

Everglades West Gulf of Mexico (Collier 4 1 19-0501 Southwest Coast Collier 8064 Coast County; Marco Island)

Everglades West 2 1 09-2718 Southwest Coast Collier, Monroe 8065 Southwest Coast Gulf 5 Coast

Ochlockonee - St. Lake Munson/Fred Munson Slough (Below 3 1 13-0102 Leon 807 Marks George Sink Lake Munson)

Ochlockonee - St. Lake Munson/Fred Munson Slough (Below 4 1 19-0566 Leon 807 Marks George Sink Lake Munson)

Key West And Outlying 3 5 18-0266 Florida Keys Lower Keys Monroe 8073 Islands

1 5 09-0951 Florida Keys Lower Keys Monroe 8073E South Beach (KW)

1 5 09-0954 Florida Keys Lower Keys Monroe 8073H Smathers Beach

1 5 09-0965 Florida Keys Upper Keys Monroe 8078A Harry Harris County Park Atlantic Ocean (Monroe 3 5 18-0267 Florida Keys Lower Keys Monroe 8079 County; Cudjoe Key-Key West)

Ochlockonee - St. Lake Munson/Fred 4 1 19-0567 Leon 807C Lake Munson Marks George Sink

Ochlockonee - St. Lake Munson/Fred Munson Slough (Above 3 1 13-0103 Leon 807D Marks George Sink Lake Munson)

Ochlockonee - St. 2 1 09-1982 St. Marks River Jefferson, Leon 808 Copeland Sink Drain Marks

Atlantic Ocean (Monroe 3 5 18-0268 Florida Keys Lower Keys Monroe 8080 County; Bahia Honda- Cudjoe Key)

1 5 09-0956 Florida Keys Lower Keys Monroe 8080B Bahia Honda Oceanside

2 5 12-0438 Florida Keys Middle Keys Monroe 8081B Sombrero Beach

Southeast Coast - Biscayne Bay Atlantic Ocean (Miami- 3 4 17-0436 Miami-Dade 8089 Biscayne Bay Intracoastal Dade County; Elliot Key)

Ochlockonee - St. Lake Munson/Fred 2 1 09-1953 Leon 820 Godby Ditch Marks George Sink

Apalachicola - 2 2 09-1651 Apalachicola River Calhoun 822 Sutton Creek Chipola

2 4 10-3070 Pensacola Pensacola Bay Santa Rosa 833A Tom King Bayou

Choctawhatchee - Choctawhatchee 1 3 05-1137 Okaloosa 843B Garniers Park St. Andrew Bay

Bridge Creek (Tidal 2 5 12-0040 Perdido Perdido Bay Escambia 872B Portion)

Ochlockonee - St. Lake Munson/Fred 4 1 19-0571 Leon 878A Lake Bradford Marks George Sink Ochlockonee - St. Lake Munson/Fred 4 1 19-0572 Leon 878D Cascade Lake Marks George Sink

Ochlockonee - St. North Ochlockonee 2 1 09-1966 Gadsden, Liberty 879 Hammock Creek Marks River

Choctawhatchee - Choctawhatchee 3 3 16-0530 Walton 881A Direct Runoff to Bay St. Andrew Bay

Choctawhatchee - Choctawhatchee 3 3 16-0531 Walton 881A Direct Runoff to Bay St. Andrew Bay

Ochlockonee - St. 3 1 13-0106 Lake Lafayette Leon 883B Virginia Tributary Marks

Ochlockonee - St. North Ochlockonee 4 1 19-0573 Leon 896 Polk Creek Marks River

Ochlockonee - St. 2 1 09-1990 Telogia Creek Liberty 913 Big Creek Marks Escambia, 2 4 10-3079 Pensacola Pensacola Bay Okaloosa, Santa 915 Santa Rosa Sound Rosa

1 4 06-0615 Pensacola Pensacola Bay Santa Rosa 915B Navarre Park Hwy. 98

1 4 06-0616 Pensacola Pensacola Bay Okaloosa 915C Liza Jackson Park

1 4 06-0617 Pensacola Pensacola Bay Okaloosa 915D Marler Park

Ochlockonee - St. Lake Munson/Fred 2 1 09-1957 Leon 916 East Drainage Ditch Marks George Sink

Choctawhatchee - Choctawhatchee 2 3 10-0464 Okaloosa 917A Destin Harbor St. Andrew Bay Ochlockonee - St. 2 1 09-1941 Lake Lafayette Leon 919 Unnamed Slough Marks

Ochlockonee - St. North Ochlockonee 4 1 19-0574 Leon 921 Harvey Creek Marks River

Choctawhatchee - Choctawhatchee 3 3 16-0532 Walton 937 Mack Bayou St. Andrew Bay

Choctawhatchee - Choctawhatchee 3 3 16-0533 Holmes 94 Limestone Branch St. Andrew River

Choctawhatchee - Choctawhatchee 3 3 19-1040 Bay 950 Otter Creek St. Andrew River Ochlockonee - St. 2 1 09-1983 St. Marks River Jefferson 965 Sweetwater Branch Marks

1 Florida's waterbody classifications are defined as: 1 - Potable water supplies 2 - Shellfish propagation or harvesting 3F - Recreation, propagation, and maintenance of a healthy, well-balanced population of fish and wildlife in fresh water 3M - Recreation, propagation, and maintenance of a healthy, well-balanced population of fish and wildlife in marine water 4 - Agricultural water supplies 5 - Navigation, utility, and industrial use 2 n is equal to the number of samples. When samples are collected at the same location less than 4 days apart, the median of those res 3 Where a parameter was identified as impaired under the IWR, a priority of “medium” was assigned. Exceptions are waters where the im poses a threat to potable water or human health, which have been assigned a “high” priority, and fecal coliform impairments, which All other listings are prioritized based on the following: it is our intent that listings with a "High" priority be addressed within the next listings with a "Medium" priority be addressed within 5-10 years as resources allow, and listings with a "Low" priority be addressed w 7 PP - Planning Period (10 year period; beginning and ending date vary by group/cycle combination); Where data are presented as x/y, x 8 VP - Verified Period (7.5 year period; beginning and ending date vary by group/cycle combination); Where data are presented as x/y, x A statewide TMDL for mercury, that will address this waterbody, is scheduled to be completed in 2012. N/A = Not Applicable, does not apply, or was not assessed in the previous cycle (i.e. it's a new WBID, waterbody type change, etc.). ^ Beach advisories are based on FL Dept of Health Enterococcus criterion of >103 CFU/100mL. Water- 1998 303(d) Parameters Assessed Dissolved Concentration of Water- body Parameters of Using the Impaired Oxygen/Biology Criterion or body Type Class1 Concern Waters Rule (IWR) Pollutant of Concern Threshold Not Met

Stream 1 Fecal Coliform ≤ 400 Counts / 100 mL

Exceeds Shellfish Fecal Coliform (SEAS Evaluation & Estuary 2 Classification) Assessment Section (SEAS) thresholds

ENRN4: AGM ≤ 0.35 Estuary 2 Nutrients (Total Nitrogen) mg/L

Estuary 2 Fecal Coliform ≤ 43 MPN / 100 mL

< 21 days of beach Coastal 3M Bacteria (Beach Advisories) advisories < 21 days of beach Coastal 3M Bacteria (Beach Advisories) advisories

ENRN3: AGM ≤ 0.34 Estuary 3M Nutrients (Total Nitrogen) mg/L

< 21 days of beach Coastal 3M Bacteria (Beach Advisories) advisories

Exceeds SEAS Estuary 2 Bacteria (in Shellfish) thresholds

ENRN1: AGM ≤ 0.33 Estuary 2 Nutrients (Total Nitrogen) mg/L

< 21 days of beach Coastal 3M Bacteria (Beach Advisories) advisories Exceeds Shellfish Evaluation & Estuary 2 Bacteria (in Shellfish) Assessment Section (SEAS) thresholds

ENRN2: AGM ≤ 0.28 Estuary 2 Nutrients (Total Nitrogen) mg/L Exceeds Shellfish Fecal Coliform (SEAS Evaluation & Estuary 2 Classification) Assessment Section (SEAS) thresholds

ENRN2: AGM ≤ 0.28 Estuary 2 Nutrients (Total Nitrogen) mg/L

Estuary 2 Fecal Coliform ≤ 43 MPN / 100 mL

Estuary 2 Fecal Coliform ≤ 43 MPN / 100 mL

Estuary 2 Nutrients (Chlorophyll-a) ENRX3: PCT ≤ 6.0 µg/L

ENRX3: PCT ≤ 0.70 Estuary 2 Nutrients (Total Nitrogen) mg/L

Exceeds Shellfish Evaluation & Stream 2 Bacteria (in Shellfish) Assessment Section (SEAS) thresholds

Stream 2 Fecal Coliform ≤ 43 MPN / 100 mL

Estuary 2 Fecal Coliform ≤ 43 MPN / 100 mL

Stream 3F Fecal Coliform > 400 Counts/100 ml

Estuary 2 Fecal Coliform ≤ 43 MPN / 100 mL

Estuary 2 Fecal Coliform ≤ 43 MPN / 100 mL

Estuary 3M Fecal Coliform ≤ 400 Counts / 100 mL

Estuary 2 Fecal Coliform ≤ 43 MPN / 100 mL

Stream 2 Fecal Coliform ≤ 43 MPN / 100 mL

Estuary 2 Fecal Coliform ≤ 43 MPN / 100 mL

Estuary 3M Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Dissolved Oxygen Total Nitrogen ≥ 5.0 mg/L

Stream 2 Fecal Coliform ≤ 43 MPN / 100 mL Exceeds Shellfish Fecal Coliform (SEAS Evaluation & Estuary 2 Classification) Assessment Section (SEAS) thresholds

Exceeds Shellfish Fecal Coliform (SEAS Evaluation & Estuary 2 Classification) Assessment Section (SEAS) thresholds

Estuary 2 Fecal Coliform ≤ 43 MPN / 100 mL

Exceeds Shellfish Fecal Coliform (SEAS Evaluation & Estuary 2 Classification) Assessment Section (SEAS) thresholds

Stream 3F Coliforms Fecal Coliform ≤ 400 Counts / 100 mL

Exceeds Shellfish Fecal Coliform (SEAS Evaluation & Estuary 2 Classification) Assessment Section (SEAS) thresholds

Estuary 2 Fecal Coliform (3) ≤ 14 MPN / 100 mL

Exceeds Shellfish Fecal Coliform (SEAS Evaluation & Estuary 2 Classification) Assessment Section (SEAS) thresholds Exceeds SEAS Estuary 3M Bacteria (in Shellfish) thresholds Exceeds SEAS Estuary 2 Bacteria (in Shellfish) thresholds

Exceeds Shellfish Fecal Coliform (SEAS Evaluation & Estuary 2 Classification) Assessment Section (SEAS) thresholds

ENRO1: AGM ≤ 0.34 Estuary 2 Nutrients (Total Nitrogen) mg/L

< 21 days of beach Beach 3M Bacteria (Beach Advisories) advisories

< 21 days of beach Coastal 3M Bacteria (Beach Advisories) advisories Exceeds Shellfish Evaluation & Stream 3F Bacteria (in Shellfish) Assessment Section (SEAS) thresholds Exceeds Shellfish Evaluation & Stream 3F Bacteria (in Shellfish) Assessment Section (SEAS) thresholds Exceeds SEAS Estuary 2 Bacteria (in Shellfish) thresholds

Estuary 2 Coliforms Fecal Coliform (3) ≤ 14 MPN/100 mL

Estuary 2 Iron ≤ 0.3 mg/L

Exceeds SEAS Estuary 2 Bacteria (in Shellfish) thresholds > 400 colonies per 100 Estuary 2 Fecal Coliform mL

Estuary 2 Fecal Coliform ≤ 43 MPN/100 mL

Exceeds Shellfish Fecal Coliform (SEAS Environmental Estuary 2 Classification) Assessment Section (SEAS) thresholds

Exceeds Shellfish Fecal Coliform (SEAS Environmental Estuary 2 Classification) Assessment Section (SEAS) thresholds

Exceeds Shellfish Evaluation & Coastal 2 Bacteria (in Shellfish) Assessment Section (SEAS) thresholds

Exceeds Shellfish Fecal Coliform (SEAS Environmental Estuary 2 Classification) Assessment Section (SEAS) thresholds

Exceeds Shellfish Evaluation & Estuary 3M Bacteria (in Shellfish) Assessment Section (SEAS) thresholds Exceeds Shellfish Evaluation & Estuary 3M Bacteria (in Shellfish) Assessment Section (SEAS) thresholds Exceeds Shellfish Evaluation & Estuary 3M Bacteria (in Shellfish) Assessment Section (SEAS) thresholds Balanced natural Stream 3F Nutrients Nutrients (Macrophytes) population of flora. Exceeds SEAS Estuary 3M Bacteria (in Shellfish) thresholds

Stream 3F Iron ≤ 1.0 mg/L

Stream 3F Iron > 1.0 mg/L

Stream 3F Iron ≤ 1.0 mg/L

Pb ≤ e(1.273[lnH]- Stream 3F Lead 4.705) µg/L

Stream 3F Iron ≤ 1.0 mg/L

Pb ≤ e(1.273[lnH]- Stream 3F Lead 4.705) µg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

See subsection 62- Lake 3F Nutrients (Total Nitrogen) 303.450(2), F.A.C.

See subsection 62- Lake 3F Nutrients (Total Phosphorus) 303.450(2), F.A.C.

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L See subsection 62- Lake 3F Nutrients (Total Nitrogen) 303.450(2), F.A.C.

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.16 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.05 mg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

See subsection 62- Lake 3F Nutrients (Total Nitrogen) 303.450(2), F.A.C.

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.16 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.05 mg/L

Stream 1 Iron > 0.3 mg/L

Stream 1 Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL Stream 3F Iron ≤ 1.0 mg/L

Pb ≤ e(1.273[lnH]- Stream 3F Lead 4.705) µg/L

Exceeds the 14 #/100 Estuary 2 Fecal Coliform (3) mL criterion Exceeds Shellfish Fecal Coliform (SEAS Evaluation & Estuary 2 Classification) Assessment Section (SEAS) thresholds

Estuary 3M Nutrients (Chlorophyll-a) ≤ 11 µg/L

Dissolved Oxygen (Percent Estuary 3M Nutrients ≥ 42 % Saturation)

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Balanced natural Spring 3F Nutrients (Algal Mats) population of flora.

Spring 3F Nutrients (Nitrate-Nitrite) ≤ 0.35 mg/L

Balanced natural Spring 3F Nutrients (Algal Mats) population of flora. Spring 3F Nutrients (Nitrate-Nitrite) ≤ 0.35 mg/L

Dissolved Oxygen (Percent Lake 3F Nutrients ≥ 38 % Saturation)

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L

Exceeds Shellfish Fecal Coliform (SEAS Evaluation & Estuary 2 Classification) Assessment Section (SEAS) thresholds Exceeds Shellfish Fecal Coliform (SEAS Evaluation & Estuary 2 Classification) Assessment Section (SEAS) thresholds

Spring 3F Nutrients (Nitrate-Nitrite) ≤ 0.35 mg/L

Spring 3F Nutrients (Nitrate-Nitrite) ≤ 0.35 mg/L

Stream 2 Fecal Coliform > 400 Counts/100 ml

Exceeds the 14 #/100 Stream 2 Fecal Coliform (3) mL criterion Exceeds Shellfish Fecal Coliform (SEAS Evaluation & Estuary 2 Classification) Assessment Section (SEAS) thresholds RPS ≤ 25%, or when between 20% - 25% Stream 3F Nutrients (Algal Mats) Evaluation of Algal Autoecological Data Indicates No Imbalance

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Balanced natural Spring 3F Nutrients (Algal Mats) population of flora.

Spring 3F Nutrients (Nitrate-Nitrite) ≤ 0.35 mg/L

Exceeds Shellfish Bacteria (Shellfish Evaluation & Estuary 2 Harvesting Classification) Assessment Section (SEAS) thresholds

Estuary 2 Fecal Coliform ≤ 43 MPN/100 mL

Estuary 2 Fecal Coliform (3) ≤ 14 MPN/100 mL

Exceeds Shellfish Fecal Coliform (SEAS Evaluation & Estuary 2 Classification) Assessment Section (SEAS) thresholds

Exceeds Shellfish Bacteria (Shellfish Evaluation & Estuary 2 Harvesting Classification) Assessment Section (SEAS) thresholds

Balanced natural Spring 3F Nutrients (Algal Mats) population of flora. Spring 3F Nutrients (Nitrate-Nitrite) ≤ 0.35 mg/L

Spring 3F Nutrients (Nitrate-Nitrite) ≤ 0.35 mg/L

RPS ≤ 25%, or when between 20% - 25% Stream 3F Nutrients (Algal Mats) Evaluation of Algal Autoecological Data Indicates No Imbalance

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Average score of at least two temporally independent LVI scores ≥ 43; or either of the two most recent LVI Lake 3F Biology Nutrients scores ≥ 43; or if there are only two LVI scores and there is less than or equal to a 20 point difference.

Lake 3F Nutrients (Chlorophyll-a) ≤ 6 µg/L

Chl-a AGM ≤ 6 µg/L, TN AGM ≤ 0.93 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TN AGM ≤ 0.51 mg/L

Chl-a AGM ≤ 6 µg/L, TP AGM ≤ 0.03 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TP AGM ≤ 0.01 mg/L

Nutrients (added from Stream 3F Dissolved Oxygen < 5.0 mg/L comments) Lake 3F Nutrients (Chlorophyll-a) ≤ 6 µg/L

Chl-a AGM ≤ 6 µg/L, TN AGM ≤ 0.93 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TN AGM ≤ 0.51 mg/L

Chl-a AGM ≤ 6 µg/L, TP AGM ≤ 0.03 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TP AGM ≤ 0.01 mg/L

Stream 3F Coliforms Fecal Coliform > 400 counts per 100ml

Balanced natural Spring 3F Nutrients (Algal Mats) population of flora.

Estuary 3M Iron ≤ 0.3 mg/L

Estuary 3M Iron ≤ 0.3 mg/L

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

LVS C of C ≥ 2.5 and Stream 1 Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Lake 3F Nutrients (Chlorophyll-a) ≤ 6 µg/L Chl-a AGM ≤ 6 µg/L, TN AGM ≤ 0.93 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TN AGM ≤ 0.51 mg/L

Chl-a AGM ≤ 6 µg/L, TP AGM ≤ 0.03 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TP AGM ≤ 0.01 mg/L

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Spring 3F Nutrients (Nitrate-Nitrite) ≤ 0.35 mg/L

Spring 3F Nutrients (Nitrate-Nitrite) ≤ 0.35 mg/L

Lake 3F Fecal Coliform > 400 Counts/100 ml

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Biochemical Oxygen Lake 3F Dissolved Oxygen ≥ 5.0 mg/L Demand

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L Lake 3F Nutrients (Chlorophyll-a) ≤ 6 µg/L

Chl-a AGM ≤ 6 µg/L, TN AGM ≤ 0.93 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TN AGM ≤ 0.51 mg/L

Chl-a AGM ≤ 6 µg/L, TP AGM ≤ 0.03 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TP AGM ≤ 0.01 mg/L

Average score of at least two temporally independent LVI scores ≥ 43; or either of the two most recent LVI Lake 3F Biology Nutrients scores ≥ 43; or if there are only two LVI scores and there is less than or equal to a 20 point difference.

Lake 3F Nutrients (Chlorophyll-a) ≤ 6 µg/L

Chl-a AGM ≤ 6 µg/L, TN AGM ≤ 0.93 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TN AGM ≤ 0.51 mg/L

Chl-a AGM ≤ 6 µg/L, TP AGM ≤ 0.03 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TP AGM ≤ 0.01 mg/L Average score of at least two temporally independent LVI scores ≥ 43; or either of the two most recent LVI Lake 3F Biology Nutrients scores ≥ 43; or if there are only two LVI scores and there is less than or equal to a 20 point difference.

Lake 3F Nutrients (Chlorophyll-a) ≤ 6 µg/L

Chl-a AGM ≤ 6 µg/L, TN AGM ≤ 0.93 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TN AGM ≤ 0.51 mg/L

Chl-a AGM ≤ 6 µg/L, TP AGM ≤ 0.03 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TP AGM ≤ 0.01 mg/L

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Stream 3F Dissolved Oxygen Total Nitrogen ≥ 5.0 mg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 6 µg/L

Chl-a AGM ≤ 6 µg/L, TN AGM ≤ 0.93 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TN AGM ≤ 0.51 mg/L Chl-a AGM ≤ 6 µg/L, TP AGM ≤ 0.03 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TP AGM ≤ 0.01 mg/L

Average score of at least two temporally independent LVI scores ≥ 43; or either of the two most recent LVI Lake 3F Biology Nutrients scores ≥ 43; or if there are only two LVI scores and there is less than or equal to a 20 point difference.

Lake 3F Nutrients (Chlorophyll-a) ≤ 6 µg/L

Chl-a AGM ≤ 6 µg/L, TN AGM ≤ 0.93 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TN AGM ≤ 0.51 mg/L

Chl-a AGM ≤ 6 µg/L, TP AGM ≤ 0.03 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TP AGM ≤ 0.01 mg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L

Average score of at least two temporally independent LVI scores ≥ 43; or either of the two most recent LVI Lake 3F Biology Nutrients scores ≥ 43; or if there are only two LVI scores and there is less than or equal to a 20 point difference.

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L Lake 3F Nutrients Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 2.23 mg/L; If Chl-a has Insufficient Lake 3F Nutrients Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.27 mg/L

Lake 3F Nutrients Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has Insufficient Lake 3F Nutrients Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L Stream 3F Coliforms Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Dissolved Oxygen (Percent Lake 3F Nutrients ≥ 38 % Saturation)

Lake 3F Nutrients (Chlorophyll-a) AGM ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 2.23 mg/L; If Chl-a has insufficient or Lake 3F Nutrients (Total Nitrogen) No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.27 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.49 mg/L; If Chl-a has insufficient or Lake 3F Nutrients (Total Phosphorus) No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.05 mg/L

Average score of at least two temporally independent LVI scores ≥ 43; or either of the two most recent LVI Lake 3F Biology Nutrients scores ≥ 43; or if there are only two LVI scores and there is less than or equal to a 20 point difference.

Chl-a AGM ≤ 6 µg/L, TN AGM ≤ 0.93 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TN AGM ≤ 0.51 mg/L

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL > 400 colonies per 100 Stream 3F Fecal Coliform ml

Stream 3F Coliforms Fecal Coliform ≤ 400 Counts / 100 mL

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Average score of at least two temporally Lake 3F Biology Nutrients independent LVI scores ≥ 43.

Lake 3F Nutrients Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has Insufficient Lake 3F Nutrients Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has Insufficient Lake 3F Nutrients Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Average score of at least two temporally Lake 3F Biology independent LVI scores ≥ 43.

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 2.23 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.27 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.16 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.05 mg/L

Stream 3F Coliforms Fecal Coliform ≤ 400 Counts / 100 mL

Lake 3F Nutrients Nutrients (Chlorophyll-a) ≤ 20 µg/L Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has Insufficient Lake 3F Nutrients Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 2.23 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.27 mg/L

Chl-a AGM ≤ 6 µg/L, TP AGM ≤ 0.03 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TP AGM ≤ 0.01 mg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 2.23 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.27 mg/L

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.16 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.05 mg/L

Nutrients, Biochemical Estuary 3M Dissolved Oxygen Dissolved Oxygen Oxygen Demand (added < 4.0 mg/L from comments)

Estuary 2 Enterococci ≤ 130 Counts / 100 mL

Estuary 2 Fecal Coliform ≤ 43 MPN/100 mL

Estuary 2 Fecal Coliform (3) ≤ 14 MPN/100 mL

Nutrients (added from Estuary 3M Dissolved Oxygen Dissolved Oxygen < 4.0 mg/L comments)

Median TN = 1.665 Estuary 3M Nutrients Nutrients (Chlorophyll-a) mg/L

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

Total Nitrogen, Total Stream 3F Dissolved Oxygen ≥ 5.0 mg/L Phosphorus

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L Stream 3F Nutrients (Total Nitrogen) AGM ≤ 1.54 mg/L

Stream 3F Nutrients (Total Phosphorus) AGM ≤ 0.12 mg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L

Spring 3F Nutrients (Nitrate-Nitrite) ≤ 0.35 mg/L

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Estuary 2 Enterococci ≤ 130 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL Lake 3F Nutrients Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has Insufficient Lake 3F Nutrients Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L

Total Phosphorus, Stream 3F Dissolved Oxygen Biochemical Oxygen ≥ 5.0 mg/L Demand

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L

Average score of at least two temporally Lake 3F Biology Nutrients independent LVI scores ≥ 43

Cu ≤ e(0.8545[lnH]- Stream 3F Copper 1.702) µg/L

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Average score of at least two temporally independent SCI scores ≥ 40; or either of the two most recent Stream 3F Biology Nutrients SCI scores ≥ 35; or if there are only two SCI scores and there is less than or equal to a 20 point difference.

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Stream 3F Nutrients (Total Phosphorus) AGM ≤ 0.12 mg/L

ENRB5 Estuary 3M Nutrients (Chlorophyll-a) AAM ≤ 8.3 µg/L

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L Estuary 3M Nutrients (Chlorophyll-a) Median TN = 0.94 mg/L

Nutrients, Biochemical Estuary 3M Dissolved Oxygen Dissolved Oxygen Oxygen Demand (added < 4.0 mg/L from comments)

Lake 3F Fecal Coliform > 400 Counts/100 ml

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 2.23 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.27 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.16 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.05 mg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Biochemical Biochemical Oxygen Stream 3F Dissolved Oxygen ≥ 5.0 mg/L Oxygen Demand Demand

Biochemical Oxygen Stream 3F Dissolved Oxygen Dissolved Oxygen ≥ 5.0 mg/L Demand

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

Stream 3F Nutrients (Chlorophyll-a) Median TN = 0.87 mg/l

Pb ≤ e^(1.273[lnH]- Lake 3F Lead 4.705)

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.16 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.05 mg/L Average score of at least two temporally independent LVI scores ≥ 43; or either of the two most recent LVI Lake 3F Biology Nutrients scores ≥ 43; or if there are only two LVI scores and there is less than or equal to a 20 point difference.

Pb ≤ e(1.273[lnH]- Lake 3F Lead 4.705) µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has insufficient or Lake 3F Nutrients (Total Nitrogen) No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L

Estuary 3M Nutrients Nutrients (Chlorophyll-a) Median TN = 1.65 mg/L

Chl-a AGM ≤ 6 µg/L, TN AGM ≤ 0.93 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TN AGM ≤ 0.51 mg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L

Estuary 3M Nutrients Nutrients (Chlorophyll-a) Median TN = 1.11 mg/l Average score of at least two temporally independent SCI scores ≥ 40; or either of the two most recent Stream 3F Biology Nutrients SCI scores ≥ 35; or if there are only two SCI scores and there is less than or equal to a 20 point difference.

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Nutrients (Total Phosphorus) AGM ≤ 0.12 mg/L

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L

Average score of at least two temporally independent LVI scores ≥ 43; or either of the two most recent LVI Lake 3F Biology Nutrients scores ≥ 43; or if there are only two LVI scores and there is less than or equal to a 20 point difference.

Stream 3F Nutrients Nutrients (Chlorophyll-a) Median TN = 1.74 mg/L

Average score of at least two temporally Lake 3F Biology Nutrients independent LVI scores ≥ 43.

Lake 3F Nutrients Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has Insufficient Lake 3F Nutrients Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has Insufficient Lake 3F Nutrients Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L

Average score of at least two temporally Lake 3F Biology Nutrients independent LVI scores ≥ 43.

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Spring 3M Copper ≤ 3.7 µg/L

Nutrients (added from Estuary 3M Dissolved Oxygen Dissolved Oxygen < 4.0 mg/L comments)

Estuary 3M Nutrients Nutrients (Chlorophyll-a) Median TN = 1.05 mg/L

Exceeds SEAS Estuary 2 Bacteria (in Shellfish) thresholds Exceeds SEAS Estuary 2 Bacteria (in Shellfish) thresholds

< 21 days of beach Beach 3M Bacteria (Beach Advisories) advisories < 21 days of beach Beach 3M Bacteria (Beach Advisories) advisories

< 21 days of beach Beach 3M Bacteria (Beach Advisories) advisories

< 21 days of beach Beach 3M Bacteria (Beach Advisories) advisories

< 21 days of beach Beach 3M Bacteria (Beach Advisories) advisories

< 21 days of beach Beach 3M Bacteria (Beach Advisories) advisories

< 21 days of beach Beach 3M Bacteria (Beach Advisories) advisories

< 21 days of beach Beach 3M Bacteria (Beach Advisories) advisories

< 21 days of beach Beach 3M Bacteria (Beach Advisories) advisories

Estuary 3M Nutrients (Chlorophyll-a) Median TN = 0.77 Exceeds Shellfish Fecal Coliform (SEAS Evaluation & Estuary 2 Classification) Assessment Section (SEAS) thresholds

Estuary 2 Enterococci ≤ 130 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Estuary 3M Coliforms Fecal Coliform ≤ 400 Counts / 100 mL

Biochemical Oxygen Stream 3F Dissolved Oxygen Demand (added from < 5.0 mg/L comments)

Stream 3F Fecal Coliform > 400 colonies/100 ml

Average score of at least two temporally independent SCI scores ≥ 40; or either of the two most recent Stream 3F Biology Nutrients SCI scores ≥ 35; or if there are only two SCI scores and there is less than or equal to a 20 point difference.

Stream 3F Nutrients (Total Phosphorus) AGM ≤ 0.12 mg/L

Stream 3F Fecal Coliform > 400 colonies/100 ml

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25% Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

Average score of at least two temporally independent SCI scores ≥ 40; or either of the two most recent Stream 3F Biology Nutrients SCI scores ≥ 35; or if there are only two SCI scores and there is less than or equal to a 20 point difference.

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Stream 3F Nutrients (Total Phosphorus) AGM ≤ 0.12 mg/L Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.16 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.05 mg/L

Average score of at least two temporally independent LVI scores ≥ 43; or either of the two most recent LVI Lake 3F Biology Nutrients scores ≥ 43; or if there are only two LVI scores and there is less than or equal to a 20 point difference.

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L

Average score of at least two temporally independent SCI scores ≥ 40; or either of the two most recent Stream 3F Biology Nutrients SCI scores ≥ 35; or if there are only two SCI scores and there is less than or equal to a 20 point difference.

Dissolved Oxygen (Percent Stream 3F Nutrients ≥ 38 % Saturation) Stream 3F Nutrients (Total Phosphorus) AGM ≤ 0.12 mg/L

Nutrients (added from Stream 3F Dissolved Oxygen < 5.0 mg/L comments)

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Average score of at least two temporally independent LVI scores ≥ 43; or either of the two most recent LVI Lake 3F Biology Nutrients scores ≥ 43; or if there are only two LVI scores and there is less than or equal to a 20 point difference.

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.16 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.05 mg/L

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

Average score of at least two temporally independent SCI scores ≥ 40; or either of the two most recent Stream 3F Biology Nutrients SCI scores ≥ 35; or if there are only two SCI scores and there is less than or equal to a 20 point difference. Stream 3F Nutrients (Total Nitrogen) AGM ≤ 1.65 mg/L

Stream 3F Nutrients (Total Phosphorus) AGM ≤ 0.49 mg/L

Median TN = 1.81 and Stream 3F Nutrients Nutrients (Chlorophyll-a) TP = 0.13 mg/l

Estuary 3M Fecal Coliform ≤ 400 Counts / 100 mL

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

Lake 3F Nutrients (Chlorophyll-a) ≤ 6 µg/L

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

≤ 20 µg/L; > 3.2 to ≤ 20 Stream 3F Nutrients (Chlorophyll-a) µg/L is a site specific interpretation Stream 3F Nutrients (Total Phosphorus) AGM ≤ 0.49 mg/L

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Estuary 3M Iron ≤ 0.3 mg/L

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Estuary 2 Fecal Coliform ≤ 43 MPN/100 mL

Estuary 2 Fecal Coliform ≤ 43 MPN/100 mL

Estuary 3M Nutrients (Chlorophyll-a) Median TN = 1.05 mg/L

Dissolved Oxygen (Percent Estuary 3M Nutrients ≥ 42 % Saturation)

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

Average score of at least two temporally independent SCI scores ≥ 40; or either of the two most recent Stream 3F Biology Nutrients SCI scores ≥ 35; or if there are only two SCI scores and there is less than or equal to a 20 point difference. Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Stream 3F Nutrients (Total Phosphorus) AGM ≤ 0.12 mg/L

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Estuary 3M Lead Included on Cycle 1 List

Estuary 3M Copper ≤ 3.7 µg/L

Estuary 3M Iron ≤ 0.3 mg/L Estuary 3M Enterococci ≤ 130 Counts / 100 mL

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Fecal Coliform > 400 counts per 100ml

Stream 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L

Stream 3F Fecal Coliform > 400 colonies/100 ml

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 2.23 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.27 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.16 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.05 mg/L

Estuary 3M Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Spring 3F Nutrients (Nitrate-Nitrite) ≤ 0.35 mg/L

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

RPS ≤ 25%, or when between 20% - 25% Stream 3F Nutrients (Algal Mats) Evaluation of Algal Autoecological Data Indicates No Imbalance

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Nutrients (added from Stream 3F Dissolved Oxygen Dissolved Oxygen < 5.0 mg/L comments)

Stream 3F Nutrients Nutrients (Chlorophyll-a) Median TN = 2.4 mg/L

Stream 3F Coliforms Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Nutrients (Total Nitrogen) AGM ≤ 1.65 mg/L

Un-ionized Stream 3F Un-ionized Ammonia ≤ 0.02 mg/L as NH3 Ammonia

Lake 3F Nutrients Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 2.23 mg/L; If Chl-a has Insufficient Lake 3F Nutrients Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.27 mg/L Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.16 mg/L; If Chl-a has Insufficient Lake 3F Nutrients Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.05 mg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 6 µg/L

Chl-a AGM ≤ 6 µg/L, TN AGM ≤ 0.93 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TN AGM ≤ 0.51 mg/L

Chl-a AGM ≤ 6 µg/L, TP AGM ≤ 0.03 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TP AGM ≤ 0.01 mg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 2.23 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.27 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.16 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.05 mg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

Total Nitrogen, Biochemical Stream 3F Dissolved Oxygen Dissolved Oxygen ≥ 5.0 mg/L Oxygen Demand

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Estuary 3M Enterococci ≤ 130 Counts / 100 mL Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

Stream 3F Dissolved Oxygen < 5.0 mg/L

Spring 3F Nutrients (Nitrate-Nitrite) ≤ 0.35 mg/L

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

Nutrients (added from Estuary 3M Dissolved Oxygen < 4.0 mg/L comments)

Estuary 3M Nutrients (Chlorophyll-a) Median TN = 1.11 mg/L

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL Stream 3F Fecal Coliform > 400 colonies/100 ml

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Biochemical Oxygen Estuary 3F Dissolved Oxygen Demand (added from < 4.0 mg/L comments)

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL Estuary 3M Enterococci ≤ 130 Counts / 100 mL

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Coliforms Fecal Coliform > 400 colonies/100 ml

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Stream 3F Fecal Coliform > 400 colonies/100 ml

Nutrients (added from Estuary 3M Dissolved Oxygen < 4.0 mg/L comments)

Estuary 3M Nutrients (Chlorophyll-a) Median TN = 1.14 mg/L

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL Total Nitrogen, Total Estuary 3M Dissolved Oxygen Phosphorus, Biochemical ≥ 4.0 mg/L Oxygen Demand

Estuary 3M Nutrients (Chlorophyll-a) ≤ 15 µg/L

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

Average score of at least two temporally Lake 3F Biology Nutrients independent LVI scores ≥ 43.

Lake 3F Nutrients (Chlorophyll-a) ≤ 6 µg/L

Chl-a AGM ≤ 6 µg/L, TN AGM ≤ 0.93 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TN AGM ≤ 0.51 mg/L

Chl-a AGM ≤ 6 µg/L, TP AGM ≤ 0.03 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TP AGM ≤ 0.01 mg/L

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL Total Phosphorus, Estuary 3M Dissolved Oxygen Biochemical Oxygen ≥ 4.0 mg/L Demand

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

Estuary 2 Enterococci ≤ 130 Counts / 100 mL

Estuary 2 Fecal Coliform ≤ 43 MPN/100 mL

Estuary 2 Fecal Coliform (3) ≤ 14 MPN/100 mL

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

ENRB5 Estuary 3M Nutrients (Chlorophyll-a) AAM ≤ 8.3 µg/L

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Estuary 2 Enterococci ≤ 130 Counts / 100 mL

Estuary 2 Fecal Coliform ≤ 43 MPN/100 mL

Estuary 2 Fecal Coliform (3) ≤ 14 MPN/100 mL

Average score of at least two temporally independent LVI scores ≥ 43; or either of the two most recent LVI Lake 3F Biology Nutrients scores ≥ 43; or if there are only two LVI scores and there is less than or equal to a 20 point difference.

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L

Stream 3F Dissolved Oxygen < 5.0 mg/L

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

Lake 3F Nutrients (Chlorophyll-a) ≤ 6 µg/L

Chl-a AGM ≤ 6 µg/L, TN AGM ≤ 0.93 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TN AGM ≤ 0.51 mg/L

Chl-a AGM ≤ 6 µg/L, TP AGM ≤ 0.03 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TP AGM ≤ 0.01 mg/L

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

Nutrients (added from Estuary 3M Dissolved Oxygen < 4.0 mg/L comments)

Estuary 3M Nutrients (Chlorophyll-a) Median TN = 1.23 mg/l Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Nutrients (Total Phosphorus) AGM ≤ 0.12 mg/L

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.16 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.05 mg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 6 µg/L

Chl-a AGM ≤ 6 µg/L, TN AGM ≤ 0.93 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TN AGM ≤ 0.51 mg/L

Estuary 3M Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

Estuary 3M Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform > 400 counts per 100ml

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Stream 3F Nutrients (Total Phosphorus) AGM ≤ 0.49 mg/L Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

Stream 3F Coliforms Fecal Coliform ≤ 400 Counts / 100 mL

Estuary 2 Enterococci ≤ 130 Counts / 100 mL

Estuary 2 Fecal Coliform ≤ 43 MPN/100 mL

Estuary 2 Fecal Coliform (3) ≤ 14 MPN/100 mL

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Estuary 3M Enterococci ≤ 130 Counts / 100 mL Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Estuary 2 Iron ≤ 0.3 mg/L

Exceeds Shellfish Fecal Coliform (SEAS Evaluation & Estuary 2 Classification) Assessment Section (SEAS) thresholds

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

> 400 colonies per 100 Lake 1 Fecal Coliform ml

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

> 400 colonies per 100 Stream 3F Fecal Coliform ml

Stream 3F Fecal Coliform > 400 Counts/100 ml

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL Stream 1 Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Coliforms Fecal Coliform ≤ 400 Counts / 100 mL

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

ENRB8: AAM ≤ 8.8 Estuary 3M Nutrients (Chlorophyll-a) µg/L

Dissolved Oxygen (Percent Estuary 3M Nutrients ≥ 42 % Saturation)

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

Estuary 3M Nutrients (Chlorophyll-a) AGM ≤ 11 µg/L

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

RPS ≤ 25%, or when between 20% - 25% Stream 3F Nutrients (Algal Mats) Evaluation of Algal Autoecological Data Indicates No Imbalance

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL Stream 3F Iron ≤ 1.0 mg/L

Average score of at least two temporally independent LVI scores ≥ 43; or either of the two most recent LVI Lake 3F Biology Nutrients scores ≥ 43; or if there are only two LVI scores and there is less than or equal to a 20 point difference.

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 2.23 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.27 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.16 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.05 mg/L

TN = 1.52 mg/L; TP = Stream 3F Nutrients (Chlorophyll-a) 0.07 mg/L

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Stream 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

> 400 colonies per 100 Stream 3F Fecal Coliform ml

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Coliforms Fecal Coliform ≤ 400 Counts / 100 mL

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

> 400 colonies per 100 Stream 3F Fecal Coliform ml

Stream 1 Fecal Coliform ≤ 400 Counts / 100 mL

LVS C of C ≥ 2.5 and Stream 1 Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Estuary 2 Fecal Coliform ≤ 43 MPN / 100 mL

< 21 days of beach Coastal 3M Bacteria (Beach Advisories) advisories

< 21 days of beach Coastal 3M Bacteria (Beach Advisories) advisories Estuary 3M Fecal Coliform ≤ 400 Counts / 100 mL

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

Stream 1 Dissolved Oxygen Total Phosphorus ≥ 5.0 mg/L

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

> 400 colonies per 100 Estuary 3M Fecal Coliform ml

Estuary 3M Nutrients (Chlorophyll-a) Median TN = 1.42 mg/L

Cu ≤ e(0.8545[lnH]- Stream 3F Copper 1.702) µg/L

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

> 400 colonies per 100 Stream 3F Fecal Coliform ml > 400 colonies per 100 Stream 1 Fecal Coliform ml

Biochemical Oxygen Estuary 3M Dissolved Oxygen Dissolved Oxygen ≥ 4.0 mg/L Demand

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Total Nitrogen, Total Stream 3F Dissolved Oxygen Phosphorus, Biochemical ≥ 5.0 mg/L Oxygen Demand

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

> 400 colonies per 100 Stream 1 Fecal Coliform ml Stream 3F Coliforms Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Un-ionized Ammonia ≤ 0.02 mg/L as NH3

Total Nitrogen, Total Estuary 3M Dissolved Oxygen Phosphorus, Biochemical ≥ 4.0 mg/L Oxygen Demand

Estuary 3M Fecal Coliform ≤ 400 Counts / 100 mL

Estuary 3M Nutrients Nutrients (Chlorophyll-a) ≤ 11 µg/L

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

> 400 colonies per 100 Stream 3F Coliforms Fecal Coliform ml

Lake 3F Nutrients (Chlorophyll-a) ≤ 6 µg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 6 µg/L

Chl-a AGM ≤ 6 µg/L, TN AGM ≤ 0.93 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TN AGM ≤ 0.51 mg/L

Chl-a AGM ≤ 6 µg/L, TP AGM ≤ 0.03 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TP AGM ≤ 0.01 mg/L Cu ≤ e(0.8545[lnH]- Stream 3F Copper 1.702) µg/L

Total Nitrogen, Total Stream 3F Dissolved Oxygen ≥ 5.0 mg/L Phosphorus

Pb ≤ e(1.273[lnH]- Stream 3F Lead 4.705) µg/L

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Iron ≤ 1.0 mg/L

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Estuary 3M Fecal Coliform ≤ 400 Counts / 100 mL

Biochemical Oxygen Estuary 3M Dissolved Oxygen ≥ 4.0 mg/L Demand

Estuary 3M Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

> 400 colonies per 100 Stream 3F Coliforms Fecal Coliform ml

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Exceeds Shellfish Evaluation & Estuary 2 Bacteria (in Shellfish) Assessment Section (SEAS) thresholds ENRC5: AAM ≤ 0.43 Estuary 3M Nutrients (Total Nitrogen) mg/L

Stream 1 Fecal Coliform ≤ 400 Counts / 100 mL

Estuary 3M Coliforms Fecal Coliform ≤ 400 Counts / 100 mL

Estuary 3M Nutrients Nutrients (Chlorophyll-a) ≤ 11 µg/L

Estuary 3M Coliforms Fecal Coliform ≤ 400 Counts / 100 mL

Estuary 3M Copper ≤ 3.7 µg/L

Estuary 3M Iron ≤ 0.3 mg/L

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 1 Coliforms Fecal Coliform ≤ 400 Counts / 100 mL

Nutrients (added from Stream 1 Dissolved Oxygen Dissolved Oxygen < 5.0 mg/L comments)

RPS ≤ 25%, or when between 20% - 25% Stream 1 Nutrients (Algal Mats) Evaluation of Algal Autoecological Data Indicates No Imbalance

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.16 mg/L; If Chl-a has Insufficient Lake 1 Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.05 mg/L

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL Exceeds Shellfish Evaluation & Estuary 3M Bacteria (in Shellfish) Assessment Section (SEAS) thresholds

ENRD2: AAM ≤ 8.9 Estuary 2 Nutrients Nutrients (Chlorophyll-a) µg/L

ENRD2: AAM ≤ 0.56 Estuary 2 Nutrients (Total Nitrogen) mg/L

Estuary 2 Fecal Coliform (3) ≤ 14 MPN/100 mL

Estuary 3M Nutrients (Chlorophyll-a) ≤ 11 µg/L

ENRD2: AAM ≤ 0.56 Estuary 3M Nutrients (Total Nitrogen) mg/L

Exceeds Shellfish Evaluation & Estuary 2 Bacteria (in Shellfish) Assessment Section (SEAS) thresholds

Estuary 3M Fecal Coliform ≤ 400 Counts / 100 mL

Total Nitrogen, Total Estuary 3M Dissolved Oxygen Phosphorus, Biochemical ≥ 4.0 mg/L Oxygen Demand

Estuary 3M Iron ≤ 0.3 mg/L

Estuary 3M Nutrients Nutrients (Chlorophyll-a) ≤ 11 µg/L

Estuary 3M Fecal Coliform ≤ 400 Counts / 100 mL Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Exceeds Shellfish Evaluation & Estuary 2 Bacteria (in Shellfish) Assessment Section (SEAS) thresholds

Estuary 2 Fecal Coliform (3) ≤ 14 MPN / 100 mL

> 400 colonies per 100 Estuary 2 Fecal Coliform ml Exceeds Shellfish Evaluation & Estuary 2 Bacteria (in Shellfish) Assessment Section (SEAS) thresholds

Estuary 2 Fecal Coliform (3) ≤ 14 MPN / 100 mL

ENRD7: AAM ≤ 1.02 Estuary 2 Nutrients (Total Nitrogen) mg/L

Estuary 2 Fecal Coliform (3) ≤ 14 MPN / 100 mL

Biochemical Stream 1 Dissolved Oxygen Total Nitrogen ≥ 5.0 mg/L Oxygen Demand

Stream 1 Dissolved Oxygen Dissolved Oxygen Total Nitrogen ≥ 5.0 mg/L

Stream 1 Coliforms Fecal Coliform ≤ 400 Counts / 100 mL

Stream 1 Iron < 1.0 mg/L

Stream 3F Coliforms Fecal Coliform ≤ 400 Counts / 100 mL

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25% LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

ENRD1: AAM ≤ 4.9 Estuary 3M Nutrients (Chlorophyll-a) µg/L

ENRD1: AAM ≤ 0.42 Estuary 3M Nutrients (Total Nitrogen) mg/L

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Estuary 3M Fecal Coliform ≤ 400 Counts / 100 mL

LVS C of C ≥ 2.5 or Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Estuary 3M Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

ENRD1: AAM ≤ 0.42 Estuary 3M Nutrients (Total Nitrogen) mg/L

ENRY3: AGM ≤ 4.0 Estuary 3M Nutrients (Chlorophyll-a) µg/L

Estuary 3M Enterococci ≤ 130 Counts / 100 mL Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Estuary 3M Copper ≤ 3.7 µg/L

Stream 1 Chloride ≤ 250 mg/L

LVS C of C ≥ 2.5 and Stream 1 Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Shall not be increased more than 50% above Stream 1 Specific Conductance background or to 1275 μmhos/cm, whichever is greater.

Stream 1 Chloride ≤ 250 mg/L

Shall not be increased more than 50% above Stream 1 Specific Conductance background or to 1275 μmhos/cm, whichever is greater.

ENRD8: AAM ≤ 1.08 Estuary 3M Nutrients (Total Nitrogen) mg/L

ENRD8: AAM ≤ 0.50 Estuary 3M Nutrients (Total Phosphorus) mg/L

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

Estuary 3M Nutrients (Chlorophyll-a) ≤ 11 µg/L

Biochemical Oxygen Estuary 3M Dissolved Oxygen ≥ 4.0 mg/L Demand

Estuary 3M Nutrients (Chlorophyll-a) ≤ 11 µg/L

Estuary 3M Nutrients (Chlorophyll-a) ≤ 11 µg/L Estuary 3M Iron ≤ 0.3 mg/L

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

Estuary 2 Copper ≤ 3.7 µg/L

Estuary 2 Fecal Coliform ≤ 31 MF / 100 mL

Estuary 3M Coliforms Fecal Coliform ≤ 400 Counts / 100 mL

Estuary 3M Iron ≤ 0.3 mg/L

Estuary 3M Nutrients (Chlorophyll-a) Median TN = 0.9 mg/L

Estuary 2 Fecal Coliform ≤ 43 MPN / 100 mL

Estuary 2 Fecal Coliform (3) ≤ 14 MPN / 100 mL

Estuary 3M Iron ≤ 0.3 mg/L

Estuary 3M Iron ≤ 0.3 mg/L

ENRD8: AAM ≤ 1.08 Estuary 3M Nutrients (Total Nitrogen) mg/L

Estuary 3M Iron ≤ 0.3 mg/L ENRD8: AAM ≤ 1.08 Estuary 3M Nutrients (Total Nitrogen) mg/L

Estuary 3M Nutrients (Chlorophyll-a) ≤ 11 µg/L

> 400 colonies per 100 Stream 3F Fecal Coliform ml

Exceeds Shellfish Fecal Coliform (SEAS Evaluation & Estuary 2 Classification) Assessment Section (SEAS) thresholds

Exceeds Shellfish Fecal Coliform (SEAS Evaluation & Estuary 2 Classification) Assessment Section (SEAS) thresholds

Estuary 3M Nutrients (Chlorophyll-a) Median TN = 1.34 mg/L

Estuary 3M Iron ≤ 0.3 mg/L

Estuary 2 Iron > 0.3 mg/L

Estuary 2 Nutrients (Chlorophyll-a) ≤ 11 µg/L

Exceeds Shellfish Fecal Coliform (SEAS Evaluation & Estuary 2 Classification) Assessment Section (SEAS) thresholds

ENRD4: AAM ≤ 0.67 Estuary 2 Nutrients (Total Nitrogen) mg/L

ENRD4: AAM ≤ 0.19 Estuary 2 Nutrients (Total Phosphorus) mg/L

ENRD4: AAM ≤ 6.1 Estuary 2 Nutrients (Chlorophyll-a) µg/L ENRD4: AAM ≤ 0.67 Estuary 2 Nutrients (Total Nitrogen) mg/L

Exceeds Shellfish Evaluation & Estuary 2 Bacteria (in Shellfish) Assessment Section (SEAS) thresholds

Exceeds Shellfish Fecal Coliform (SEAS Evaluation & Estuary 2 Classification) Assessment Section (SEAS) thresholds

Exceeds Shellfish Evaluation & Estuary 2 Bacteria (in Shellfish) Assessment Section (SEAS) thresholds

ENRD5: AAM ≤ 0.57 Estuary 2 Nutrients (Total Nitrogen) mg/L

Exceeds Shellfish Evaluation & Estuary 2 Bacteria (in Shellfish) Assessment Section (SEAS) thresholds

ENRD9: AAM ≤ 0.58 Estuary 2 Nutrients (Total Nitrogen) mg/L

Exceeds Shellfish Fecal Coliform (SEAS Evaluation & Estuary 2 Classification) Assessment Section (SEAS) thresholds

ENRD5: AAM ≤ 6.5 Estuary 2 Nutrients (Chlorophyll-a) µg/L ENRD5: AAM ≤ 0.57 Estuary 2 Nutrients (Total Nitrogen) mg/L

Exceeds Shellfish Fecal Coliform (SEAS Evaluation & Estuary 2 Classification) Assessment Section (SEAS) thresholds

ENRD6: AVG2 ≤ 3.7 Estuary 2 Nutrients (Chlorophyll-a) µg/L

ENRD6: AVG2 ≤ 0.44 Estuary 2 Nutrients (Total Nitrogen) mg/L

Stream 1 Fecal Coliform ≤ 400 Counts / 100 mL

Dissolved Oxygen (Percent Estuary 2 Nutrients ≥ 42 % Saturation)

Estuary 2 Fecal Coliform ≤ 43 MPN/100 mL

Estuary 2 Fecal Coliform (3) ≤ 14 MPN/100 mL

Exceeds Shellfish Fecal Coliform (SEAS Environmental Estuary 2 Classification) Assessment Section (SEAS) thresholds

Estuary 2 Nutrients (Chlorophyll-a) AGM ≤ 11 µg/L Exceeds Shellfish Evaluation & Estuary 2 Bacteria (in Shellfish) Assessment Section (SEAS) thresholds

ENRD5: AAM ≤ 0.57 Estuary 2 Nutrients (Total Nitrogen) mg/L

Dissolved Oxygen (Percent Lake 3F Nutrients ≥ 38 % Saturation)

Lake 3F Nutrients (Chlorophyll-a) AGM ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 2.23 mg/L; If Chl-a has insufficient or Lake 3F Nutrients (Total Nitrogen) No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.27 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.16 mg/L; If Chl-a has insufficient or Lake 3F Nutrients (Total Phosphorus) No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.05 mg/L

Pb ≤ e(1.273[lnH]- Stream 3F Lead 4.705) µg/L

Pb ≤ e(1.273[lnH]- Stream 3F Lead 4.705) µg/L

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Estuary 3M Enterococci ≤ 130 Counts / 100 mL Nutrients (added from Stream 3F Dissolved Oxygen < 5.0 mg/L comments)

> 400 colonies per 100 Stream 3F Fecal Coliform ml

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Estuary 3M Fecal Coliform ≤ 400 Counts / 100 mL

Blackwater 3F Fecal Coliform ≤ 400 Counts / 100 mL

ENRBB1: LTAAM ≤ 5.4 Estuary 3M Nutrients Nutrients (Chlorophyll-a) µg/L

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Estuary 3M Coliforms Fecal Coliform ≤ 400 Counts / 100 mL

Estuary 3M Iron ≤ 0.3 mg/L

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Estuary 3M Copper ≤ 3.7 µg/L

Estuary 3M Thallium < 6.3 μg/L

Estuary 3M Iron > 0.3 mg/l Estuary 3M Thallium < 6.3 μg/L

Estuary 3M Iron > 0.3 mg/l

Estuary 3M Fecal Coliform ≤ 400 Counts / 100 mL

Estuary 3M Iron ≤ 0.3 mg/L

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Pb ≤ e(1.273[lnH]- Stream 3F Lead 4.705) µg/L

Estuary 3M Iron ≤ 0.3 mg/L

Estuary 3M Iron ≤ 0.3 mg/L

Estuary 3M Copper ≤ 3.7 µg/L

Estuary 3M Iron ≤ 0.3 mg/L

ENRBB1: LTAAM ≤ 5.4 Estuary 3M Nutrients (Chlorophyll-a) µg/L

Stream 3F Iron ≤ 1.0 mg/L

> 400 colonies per 100 Stream 3F Fecal Coliform ml > 400 colonies per 100 Stream 3F Fecal Coliform ml Stream 3F Iron ≤ 1.0 mg/L

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

> 400 colonies per 100 Stream 3F Fecal Coliform ml

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Pb ≤ e(1.273[lnH]- Stream 3F Lead 4.705) µg/L

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

> 400 colonies per 100 Stream 3F Fecal Coliform ml

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Pb ≤ e(1.273[lnH]- Stream 3F Lead 4.705) µg/L

> 400 colonies per 100 Stream 3F Fecal Coliform ml Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Pb ≤ e^(1.273[lnH]- Stream 3F Lead 4.705)

Stream 3F Iron ≤ 1.0 mg/L

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Estuary 3M Iron ≤ 0.3 mg/L

ENRBB1: LTAAM ≤ 5.4 Estuary 3M Nutrients (Chlorophyll-a) µg/L

> 400 colonies per 100 Stream 3F Fecal Coliform ml

Estuary 3M Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Dissolved Oxygen (Percent Estuary 3M Nutrients ≥ 42 % Saturation)

Estuary 3M Nutrients (Chlorophyll-a) AGM ≤ 11 µg/L

Estuary 3M Fecal Coliform ≤ 400 Counts / 100 mL

Estuary 3M Iron ≤ 0.3 mg/L Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Exceeds SEAS Estuary 2 Bacteria (in Shellfish) thresholds > 400 colonies per 100 Stream 3F Fecal Coliform ml

Stream 3F Iron ≤ 1.0 mg/L

Pb ≤ e(1.273[lnH]- Stream 3F Lead 4.705) µg/L

Stream 3F Iron ≤ 1.0 mg/L Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

ENRS1 Estuary 3M Nutrients (Chlorophyll-a) AGM ≤ 6.2 µg/L

ENRS1 Estuary 3M Nutrients (Total Nitrogen) AGM ≤ 0.72 mg/L

Estuary 3M Copper Copper ≤ 3.7 µg/L

Estuary 3M Nutrients (Chlorophyll-a) ≤ 11 µg/L

Estuary 3M Iron ≤ 0.3 mg/L

Exceeds Shellfish Bacteria (Shellfish Evaluation & Estuary 2 Harvesting Classification) Assessment Section (SEAS) thresholds

Estuary 3M Iron ≤ 0.3 mg/L

Exceeds Shellfish Bacteria (Shellfish Evaluation & Estuary 2 Harvesting Classification) Assessment Section (SEAS) thresholds

ENRT1 Estuary 3M Nutrients (Total Nitrogen) AGM ≤ 0.65 mg/L

Exceeds Shellfish Bacteria (Shellfish Evaluation & Estuary 2 Harvesting Classification) Assessment Section (SEAS) thresholds ENRY10 Estuary 3M Nutrients (Chlorophyll-a) AAM ≤ 4.5 µg/L

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

> 400 colonies per 100 Stream 3F Fecal Coliform ml > 400 colonies per 100 Stream 3F Fecal Coliform ml Pb ≤ e^(1.273[lnH]- Stream 3F Lead 4.705)

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Iron ≤ 1.0 mg/L

Exceeds Shellfish Bacteria (Shellfish Evaluation & Estuary 2 Harvesting Classification) Assessment Section (SEAS) thresholds

Estuary 2 Fecal Coliform (3) ≤ 14 MPN / 100 mL

Nutrients (added from Stream 3F Dissolved Oxygen < 5.0 mg/l comments)

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Lead > e(1.273[LNH]-4.705)

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Lead > e(1.273[LNH]-4.705)

Exceeds SEAS Estuary 3M Bacteria (in Shellfish) thresholds

Exceeds SEAS Stream 2 Bacteria (in Shellfish) thresholds

Stream 2 Fecal Coliform > 400 colonies/100 ml

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Exceeds SEAS Estuary 2 Bacteria (in Shellfish) thresholds

Stream 3F Iron Iron ≤ 1.0 mg/L Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Exceeds SEAS Estuary 2 Bacteria (in Shellfish) thresholds

Exceeds SEAS Estuary 2 Bacteria (in Shellfish) thresholds

Estuary 2 Fecal Coliform > 400 colonies/100 ml

Stream 3F Fecal Coliform > 400 colonies/100 ml

Exceeds SEAS Estuary 2 Bacteria (in Shellfish) thresholds Exceeds SEAS Estuary 2 Bacteria (in Shellfish) thresholds Exceeds Shellfish Bacteria (Shellfish Evaluation & Estuary 2 Harvesting Classification) Assessment Section (SEAS) thresholds

Dissolved Oxygen (Percent Estuary 3M Nutrients ≥ 42 % Saturation)

Estuary 3M Nutrients (Chlorophyll-a) ≤ 11 µg/L

ENRL6: PCT ≤ 0.61 Estuary 3M Nutrients (Total Nitrogen) mg/L

Exceeds Shellfish Bacteria (Shellfish Evaluation & Estuary 2 Harvesting Classification) Assessment Section (SEAS) thresholds Pb ≤ e^(1.273[lnH]- Lake 3F Lead 4.705) Pb ≤ e^(1.273[lnH]- Lake 3F Lead 4.705)

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Pb ≤ e^(1.273[lnH]- Stream 3F Lead 4.705)

Estuary 2 Fecal Coliform ≤ 43 MPN/100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Pb ≤ e^(1.273[lnH]- Lake 3F Lead 4.705)

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 2.23 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.27 mg/L Biochemical Stream 3F Dissolved Oxygen Total Phosphorus ≥ 5.0 mg/L Oxygen Demand

Average score of at least two temporally independent SCI scores ≥ 40; or either of the two most recent Stream 3F Biology Nutrients SCI scores ≥ 35; or if there are only two SCI scores and there is less than or equal to a 20 point difference.

Stream 3F Nutrients (Total Phosphorus) AGM ≤ 0.12 mg/L

Shall not be increased more than 50% above Stream 3F Specific Conductance background or to 1275 μmhos/cm, whichever is greater.

Exceeds Shellfish Bacteria (Shellfish Evaluation & Estuary 2 Harvesting Classification) Assessment Section (SEAS) thresholds

Biochemical Total Nitrogen, Total Stream 3F Dissolved Oxygen ≥ 5.0 mg/L Oxygen Demand Phosphorus

Total Nitrogen, Total Stream 3F Dissolved Oxygen Dissolved Oxygen ≥ 5.0 mg/L Phosphorus

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Iron ≤ 1.0 mg/L

Shall not be increased more than 50% above Stream 3F Specific Conductance background or to 1275 μmhos/cm, whichever is greater. Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Stream 3F Nutrients (Total Phosphorus) AGM ≤ 0.12 mg/L

Nutrients (added from Stream 3F Dissolved Oxygen < 5.0 mg/l comments)

Stream 3F Iron ≤ 1.0 mg/L

Exceeds Shellfish Bacteria (Shellfish Evaluation & Estuary 2 Harvesting Classification) Assessment Section (SEAS) thresholds

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Iron ≤ 1.0 mg/L

Estuary 2 Fecal Coliform ≤ 43 MPN/100 mL

ENRT4 Estuary 2 Nutrients (Chlorophyll-a) AGM ≤ 4.3 µg/L

Dissolved Oxygen (Percent Estuary 2 Nutrients ≥ 42 % Saturation)

ENRT4 Estuary 2 Nutrients (Chlorophyll-a) AGM ≤ 4.3 µg/L Pb ≤ e(1.273[lnH]- Lake 3F Lead 4.705) µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 2.23 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.27 mg/L

Dissolved Oxygen (Percent Lake 3F Nutrients ≥ 38 % Saturation)

Pb ≤ e(1.273[lnH]- Lake 3F Lead 4.705) µg/L

Nutrients (added from Stream 3F Dissolved Oxygen < 5.0 mg/l comments)

> 400 colonies per 100 Stream 3F Fecal Coliform ml

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Nutrients (Chlorophyll-a) TP = 0.072 mg/l

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

RPS ≤ 25%, or when between 20% - 25% Stream 3F Nutrients (Algal Mats) Evaluation of Algal Autoecological Data Indicates No Imbalance

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Iron ≤ 1.0 mg/L Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 2.23 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.27 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.16 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.05 mg/L

Biochemical Stream 3F Dissolved Oxygen ≥ 5.0 mg/L Oxygen Demand

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Stream 3F Nutrients (Total Nitrogen) AGM ≤ 1.54 mg/L

Stream 3F Nutrients (Total Phosphorus) AGM ≤ 0.12 mg/L

Total Nitrogen, Biochemical Stream 3F Dissolved Oxygen ≥ 5.0 mg/L Oxygen Demand

Pb ≤ e^(1.273[lnH]- Stream 3F Lead Lead 4.705) Pb ≤ e^(1.273[lnH]- Lake 3F Lead 4.705)

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL Estuary 3M Nutrients (Chlorophyll-a) ≤ 11 µg/L

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Stream 3F Nutrients (Total Phosphorus) AGM ≤ 0.12 mg/L

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Estuary 3M Copper ≤ 3.7 µg/L

Nutrients, Biochemical Estuary 3M Dissolved Oxygen Oxygen Demand (added < 4.0 mg/L from comments)

Median TN = 1.00 mg/L Estuary 3M Nutrients (Chlorophyll-a) Median TP = 0.192 mg/L Dissolved Oxygen (Percent Stream 3F Nutrients ≥ 38 % Saturation)

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Stream 3F Nutrients (Total Phosphorus) AGM ≤ 0.12 mg/L

Stream 3F Coliforms Fecal Coliform > 400 Counts/100 ml

Stream 3F Fecal Coliform > 400 Counts/100 ml

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Average score of at least two temporally independent LVI scores ≥ 43; or either of the two most recent LVI Lake 3F Biology Nutrients scores ≥ 43; or if there are only two LVI scores and there is less than or equal to a 20 point difference.

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 2.23 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.27 mg/L Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.16 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.05 mg/L

Average score of at least two temporally independent SCI scores ≥ 40; or either of the two most recent Stream 3F Biology Nutrients SCI scores ≥ 35; or if there are only two SCI scores and there is less than or equal to a 20 point difference.

Stream 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Stream 3F Nutrients (Total Nitrogen) AGM ≤ 1.54 mg/L

Stream 3F Nutrients (Total Phosphorus) AGM ≤ 0.12 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.16 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.05 mg/L

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform > 400 Counts/100 ml Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.16 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.05 mg/L

Total Nitrogen, Total Lake 3F Dissolved Oxygen Phosphorus, Biochemical ≥ 5.0 mg/L Oxygen Demand

Average score of at least two temporally independent SCI scores ≥ 40; or either of the two most recent Stream 3F Biology Nutrients SCI scores ≥ 35; or if there are only two SCI scores and there is less than or equal to a 20 point difference.

> 29 NTUs above Lake 3F Turbidity background

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform > 400 Counts/100 ml Lake 3F Fecal Coliform > 400 Counts/100 ml

Spring 3F Nutrients (Nitrate-Nitrite) ≤ 0.35 mg/L

Nutrients (added from Stream 3F Dissolved Oxygen < 5.0 mg/L comments)

Stream 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Stream 3F Nutrients (Total Nitrogen) AGM ≤ 1.54 mg/L Stream 3F Nutrients (Total Phosphorus) AGM ≤ 0.12 mg/L

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Stream 3F Nutrients (Total Nitrogen) AGM ≤ 1.54 mg/L

Total Nitrogen, Total Stream 3F Dissolved Oxygen ≥ 5.0 mg/L Phosphorus

Total Nitrogen, Total Stream 3F Dissolved Oxygen ≥ 5.0 mg/L Phosphorus

Pb ≤ e(1.273[lnH]- Stream 3F Lead 4.705) µg/L

Pb ≤ e(1.273[lnH]- Stream 3F Lead 4.705) µg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 6 µg/L Chl-a AGM ≤ 6 µg/L, TN AGM ≤ 0.93 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TN AGM ≤ 0.51 mg/L

Chl-a AGM ≤ 6 µg/L, TP AGM ≤ 0.03 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TP AGM ≤ 0.01 mg/L

Stream 3F Dissolved Oxygen Total Nitrogen ≥ 5.0 mg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L

Lake 3F Pesticides (in fish tissue) NA

RPS ≤ 25%, or when between 20% - 25% Spring 3F Nutrients (Algal Mats) Evaluation of Algal Autoecological Data Indicates No Imbalance

Spring 3F Nutrients (Nitrate-Nitrite) ≤ 0.35 mg/L

Spring 3F Nutrients (Nitrate-Nitrite) ≤ 0.35 mg/L

Stream 3F Dissolved Oxygen Total Nitrogen ≥ 5.0 mg/L

Nutrients (added from Stream 3F Dissolved Oxygen < 5.0 mg/L comments) Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Silver ≤ 0.07 µg/L

LVS C of C ≥ 2.5 and Stream 1 Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Biochemical Stream 3F Dissolved Oxygen Total Nitrogen ≥ 5.0 mg/L Oxygen Demand

Stream 3F Silver ≤ 0.07 µg/L

Stream 3F Iron ≤ 1.0 mg/L

Stream 1 Fecal Coliform ≤ 400 Counts / 100 mL

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

LVS C of C ≥ 2.5 and Stream 1 Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Stream 1 Nutrients (Total Nitrogen) AGM ≤ 1.54 mg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.16 mg/L; If Chl-a has insufficient or Lake 1 Nutrients (Total Phosphorus) No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.05 mg/L

Total Nitrogen, Biochemical Stream 1 Dissolved Oxygen ≥ 5.0 mg/L Oxygen Demand

Stream 3F Iron ≤ 1.0 mg/L LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Lake 3F Nutrients (Chlorophyll-a) AGM ≤ 6 µg/L

Chl-a AGM ≤ 6 µg/L, TN AGM ≤ 0.93 mg/L; If Chl-a has insufficient or Lake 3F Nutrients (Total Nitrogen) No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TN AGM ≤ 0.51 mg/L

Chl-a AGM ≤ 6 µg/L, TP AGM ≤ 0.03 mg/L; If Chl-a has insufficient or Lake 3F Nutrients (Total Phosphorus) No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TP AGM ≤ 0.01 mg/L

RPS ≤ 25%, or when between 20% - 25% Stream 3F Nutrients (Algal Mats) Evaluation of Algal Autoecological Data Indicates No Imbalance

Lake 3F Nutrients (Chlorophyll-a) AGM ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 2.23 mg/L; If Chl-a has insufficient or Lake 3F Nutrients (Total Nitrogen) No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.27 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.16 mg/L; If Chl-a has insufficient or Lake 3F Nutrients (Total Phosphorus) No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.05 mg/L LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

ENRAA11 Estuary 2 Nutrients (Chlorophyll-a) AGM ≤ 2.5 µg/L

ENRAA11 Estuary 2 Nutrients (Total Nitrogen) AGM ≤ 1.14 mg/L

ENRAA11 Estuary 2 Nutrients (Total Phosphorus) AGM ≤ 0.034 mg/L

Exceeds Shellfish Bacteria (Shellfish Evaluation & Estuary 2 Harvesting Classification) Assessment Section (SEAS) thresholds

ENRAA12 Estuary 2 Nutrients (Chlorophyll-a) AGM ≤ 3.4 µg/L

ENRAA12 Estuary 2 Nutrients (Total Nitrogen) AGM ≤ 0.65 mg/L Exceeds Shellfish Fecal Coliform (SEAS Evaluation & Estuary 2 Classification) Assessment Section (SEAS) thresholds

ENRAA13 Estuary 2 Nutrients (Chlorophyll-a) AGM ≤ 4.0 µg/L

Stream 3F Dissolved Oxygen Total Nitrogen ≥ 5.0 mg/L

Estuary 3M Dissolved Oxygen Total Nitrogen ≥ 4.0 mg/L

Estuary 3M Nutrients (Chlorophyll-a) ≤ 11 µg/L

Total Nitrogen, Biochemical Stream 3F Dissolved Oxygen ≥ 5.0 mg/L Oxygen Demand

Exceeds Shellfish Bacteria (Shellfish Evaluation & Estuary 2 Harvesting Classification) Assessment Section (SEAS) thresholds

Estuary 2 Fecal Coliform (3) ≤ 14 MPN/100 mL

Estuary 2 Fecal Coliform (3) ≤ 14 MPN/100 mL Exceeds Shellfish Fecal Coliform (SEAS Evaluation & Estuary 2 Classification) Assessment Section (SEAS) thresholds

Exceeds Shellfish Bacteria (Shellfish Evaluation & Estuary 2 Harvesting Classification) Assessment Section (SEAS) thresholds Exceeds Shellfish Bacteria (Shellfish Evaluation & Estuary 2 Harvesting Classification) Assessment Section (SEAS) thresholds Exceeds Shellfish Bacteria (Shellfish Evaluation & Estuary 2 Harvesting Classification) Assessment Section (SEAS) thresholds

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.16 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.05 mg/L

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Nutrients (added from Stream 3F Dissolved Oxygen < 5.0 mg/L comments)

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.16 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.05 mg/L Lake 3F Nutrients (Chlorophyll-a) AGM ≤ 20 µg/L

Spring 3F Nutrients (Nitrate-Nitrite) ≤ 0.35 mg/L

Spring 3F Nutrients (Nitrate-Nitrite) ≤ 0.35 mg/L

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Lake 3F Nutrients (Chlorophyll-a) AGM ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has insufficient or Lake 3F Nutrients (Total Phosphorus) No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L

Lake 3F Nutrients (Chlorophyll-a) AGM ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has insufficient or Lake 3F Nutrients (Total Nitrogen) No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has insufficient or Lake 3F Nutrients (Total Phosphorus) No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Lake 3F Nutrients (Chlorophyll-a) AGM ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has insufficient or Lake 3F Nutrients (Total Phosphorus) No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L

Lake 3F Fecal Coliform ≤ 400 Counts / 100 mL

Average score of at least two temporally Lake 3F Biology Nutrients independent LVI scores ≥ 43

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Lake 3F Nutrients (Chlorophyll-a) AGM ≤ 6 µg/L Chl-a AGM ≤ 6 µg/L, TN AGM ≤ 0.93 mg/L; If Chl-a has insufficient or Lake 3F Nutrients (Total Nitrogen) No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TN AGM ≤ 0.51 mg/L

Chl-a AGM ≤ 6 µg/L, TP AGM ≤ 0.03 mg/L; If Chl-a has insufficient or Lake 3F Nutrients (Total Phosphorus) No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TP AGM ≤ 0.01 mg/L

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Lake 3F Nutrients (Chlorophyll-a) AGM ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has insufficient or Lake 3F Nutrients (Total Nitrogen) No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L

Lake 3F Nutrients (Chlorophyll-a) AGM ≤ 20 µg/L

Lake 3F Fecal Coliform ≤ 400 Counts / 100 mL Average score of at least two temporally independent LVI scores ≥ 43; or either of the two most recent LVI Lake 3F Biology Nutrients scores ≥ 43; or if there are only two LVI scores and there is less than or equal to a 20 point difference.

Lake 3F Nutrients (Chlorophyll-a) AGM ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has insufficient or Lake 3F Nutrients (Total Nitrogen) No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has insufficient or Lake 3F Nutrients (Total Phosphorus) No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has insufficient or Lake 3F Nutrients (Total Phosphorus) No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L

Average score of at least two temporally independent LVI scores ≥ 43; or either of the two most recent LVI Lake 3F Biology Nutrients scores ≥ 43; or if there are only two LVI scores and there is less than or equal to a 20 point difference.

Lake 3F Nutrients (Chlorophyll-a) AGM ≤ 20 µg/L Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has insufficient or Lake 3F Nutrients (Total Nitrogen) No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has insufficient or Lake 3F Nutrients (Total Phosphorus) No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Stream 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Silver ≤ 0.07 µg/L

Stream 3F Fecal Coliform > 400 per 100 ml

Stream 3F Fecal Coliform > 400 per 100 ml

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Lake 3F Nutrients (Chlorophyll-a) AGM ≤ 20 µg/L Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has insufficient or Lake 3F Nutrients (Total Phosphorus) No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Exceeds Shellfish Fecal Coliform (SEAS Evaluation & Estuary 2 Classification) Assessment Section (SEAS) thresholds

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Stream 3F Nutrients (Total Phosphorus) AGM ≤ 0.12 mg/L

Exceeds Shellfish Fecal Coliform (SEAS Evaluation & Estuary 2 Classification) Assessment Section (SEAS) thresholds

Exceeds Shellfish Fecal Coliform (SEAS Evaluation & Estuary 2 Classification) Assessment Section (SEAS) thresholds

Estuary 3M Copper > 3.7 µg/L

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Estuary 3M Copper ≤ 3.7 µg/L LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Iron Iron ≤ 1.0 mg/L

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

LVS C of C ≥ 2.5 and Stream 1 Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Total Nitrogen, Total Stream 1 Dissolved Oxygen ≥ 5.0 mg/L Phosphorus

LVS C of C ≥ 2.5 and Stream 1 Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Stream 1 Nutrients (Total Nitrogen) AGM ≤ 1.54 mg/L

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 1 Chloride ≤ 250 mg/L

LVS C of C ≥ 2.5 and Stream 1 Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Total Nitrogen, Total Stream 1 Dissolved Oxygen Phosphorus, Biochemical ≥ 5.0 mg/L Oxygen Demand

Estuary 3M Iron ≤ 0.3 mg/L Lake 1 Nutrients Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 2.23 mg/L; If Chl-a has Insufficient Lake 1 Nutrients Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.27 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.16 mg/L; If Chl-a has Insufficient Lake 1 Nutrients Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.05 mg/L

Stream 3F Fecal Coliform > 400 colonies/100 ml

Stream 3F Iron ≤ 1.0 mg/L

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Coliforms Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform > 400 colonies/100 ml

Biochemical Oxygen Stream 3F Dissolved Oxygen Dissolved Oxygen ≥ 5.0 mg/L Demand

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Stream 3F Nutrients (Total Phosphorus) AGM ≤ 0.12 mg/L Nutrients (added from Stream 3F Dissolved Oxygen DO < 5 mg/L comments)

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 2.23 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.27 mg/L Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.16 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.05 mg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 2.23 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.27 mg/L Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L

Lake 3F Silver ≤ 0.07 µg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L

Lake 3F Fecal Coliform ≤ 400 Counts / 100 mL

Pb ≤ e(1.273[lnH]- Lake 3F Lead 4.705) µg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.16 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.05 mg/L Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 2.23 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.27 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.16 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.05 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 6 µg/L

Chl-a AGM ≤ 6 µg/L, TN AGM ≤ 0.93 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TN AGM ≤ 0.51 mg/L Chl-a AGM ≤ 6 µg/L, TP AGM ≤ 0.03 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TP AGM ≤ 0.01 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Pb ≤ e(1.273[lnH]- Lake 3F Lead 4.705) µg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 1.91 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.05 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.16 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.05 mg/L

Chl-a AGM ≤ 6 µg/L, TN AGM ≤ 0.93 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TN AGM ≤ 0.51 mg/L

Blackwater 3F Fecal Coliform ≤ 400 Counts / 100 mL

Pb ≤ e(1.273[lnH]- Stream 3F Lead 4.705) µg/L

Stream 3F Fecal Coliform > 400 counts per 100ml Chl-a AGM ≤ 6 µg/L, TN AGM ≤ 0.93 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TN AGM ≤ 0.51 mg/L

Pb ≤ e(1.273[lnH]- Lake 3F Lead 4.705) µg/L

Pb ≤ e(1.273[lnH]- Lake 3F Lead 4.705) µg/L

Lake 3F Copper > e(0.854[lnH]-1.465)

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Stream 3F Nutrients (Total Phosphorus) AGM ≤ 0.12 mg/L

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Nutrients Nutrients (Chlorophyll-a) ≤ 20 µg/L

Biochemical Oxygen Stream 3F Dissolved Oxygen Dissolved Oxygen ≥ 5.0 mg/L Demand

Stream 3F Nutrients Nutrients (Chlorophyll-a) ≤ 20 µg/L LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Stream 3F Nutrients (Total Phosphorus) AGM ≤ 0.12 mg/L

Biochemical Oxygen Stream 3F Dissolved Oxygen ≥ 5.0 mg/L Demand

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Exceeds Shellfish Evaluation and Estuary 3M Bacteria (in Shellfish) Assessment Section thresholds.

Stream 3F Nutrients Nutrients (Chlorophyll-a) TN = 3.03 mg/L

Total Nitrogen, Biochemical Stream 3F Dissolved Oxygen Dissolved Oxygen ≥ 5.0 mg/L Oxygen Demand

Stream 3F Coliforms Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Iron ≤ 1.0 mg/L

Stream 3F Nutrients (Total Phosphorus) AGM ≤ 0.12 mg/L

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

< 21 days of beach Beach 3M Bacteria (Beach Advisories) advisories

Estuary 3M Copper Cu > 3.7 µg/L

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

Estuary 3M Copper Cu > 3.7 µg/L Cu ≤ e(0.8545[lnH]- Lake 3F Copper 1.702) µg/L

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Nutrients (added from Stream 3F Dissolved Oxygen < 5.0 mg/l comments)

Nutrients (added from Stream 3F Dissolved Oxygen Dissolved Oxygen < 5.0 mg/l comments)

Stream 3F Nutrients Nutrients (Chlorophyll-a) Median TN = 3.10 mg/L

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Nutrients (Total Nitrogen) AGM ≤ 1.54 mg/L

Stream 3F Nutrients (Total Phosphorus) AGM ≤ 0.12 mg/L

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Stream 3F Nutrients (Total Nitrogen) AGM ≤ 1.54 mg/L LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Stream 3F Nutrients (Total Phosphorus) AGM ≤ 0.12 mg/L

Nutrients (added from Stream 3F Dissolved Oxygen Dissolved Oxygen < 5.0 mg/l comments)

Stream 3F Coliforms Fecal Coliform > 400 Counts/100 ml

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Nutrients (added from Stream 3F Dissolved Oxygen < 5.0 mg/l comments)

Stream 3F Nutrients (Chlorophyll-a) Median TP = 0.01 mg/L

TN = 2.54 mg/L; TP = Stream 3F Nutrients Nutrients (Chlorophyll-a) 0.20 mg/L

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Stream 3F Nutrients (Total Nitrogen) AGM ≤ 1.54 mg/L Stream 3F Nutrients (Total Phosphorus) AGM ≤ 0.12 mg/L

Dissolved Oxygen (Percent Stream 3F Nutrients ≥ 38 % Saturation)

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Iron ≤ 1.0 mg/L

Stream 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Stream 3F Nutrients (Total Nitrogen) AGM ≤ 1.54 mg/L

Stream 3F Nutrients (Total Phosphorus) AGM ≤ 0.12 mg/L

Nutrients (added from Stream 3F Dissolved Oxygen < 5.0 mg/l comments)

Stream 3F Iron ≤ 1.0 mg/L Nutrients (added from Stream 3F Dissolved Oxygen Dissolved Oxygen < 5.0 mg/l comments)

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

TN = 2.10 mg/L; TP = Stream 3F Nutrients Nutrients (Chlorophyll-a) 0.24 mg/L

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Stream 3F Nutrients (Total Phosphorus) AGM ≤ 0.12 mg/L

Nutrients (added from Stream 3F Dissolved Oxygen < 5.0 mg/L comments)

Stream 3F Iron ≤ 1.0 mg/L

ENRAA2: PCT ≤ 6.9 Estuary 3M Nutrients (Chlorophyll-a) µg/L

ENRAA2: PCT ≤ 6.9 Estuary 2 Nutrients (Chlorophyll-a) µg/L

Estuary 3M Copper ≤ 3.7 µg/L

ENRZ6: AGM ≤ 5.9 Estuary 3M Nutrients (Chlorophyll-a) µg/L

Estuary 3M Copper Cu > 3.7 µg/L

Estuary 3M Copper Cu > 3.7 µg/L Estuary 3M Enterococci ≤ 130 Counts / 100 mL

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

Estuary 3M Copper Cu > 3.7 µg/L

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

Lake 1 Iron ≤ 1.0 mg/L

Lake 1 Iron Iron ≤ 1.0 mg/L

Lake 1 Iron Iron ≤ 1.0 mg/L

Lake 1 Iron ≤ 1.0 mg/L

Lake 1 Iron Iron < 1.0 mg/L

Lake 1 Iron ≤ 1.0 mg/L

Nutrients (added from Stream 3F Dissolved Oxygen Dissolved Oxygen < 5.0 mg/l comments)

Stream 3F Iron ≤ 1.0 mg/L Nutrients (added from Stream 3F Dissolved Oxygen Dissolved Oxygen < 5.0 mg/l comments)

Stream 3F Coliforms Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Iron ≤ 1.0 mg/L

Nutrients (added from Stream 3F Dissolved Oxygen Dissolved Oxygen < 5.0 mg/l comments)

Stream 3F Nutrients Nutrients (Chlorophyll-a) Median TN = 1.96 mg/L

Stream 3F Iron ≤ 1.0 mg/L

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Nutrients (added from Stream 3F Dissolved Oxygen < 5.0 mg/l comments)

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

ENRAA1: AGM ≤ 2 Estuary 3M Nutrients (Chlorophyll-a) µg/L

Estuary 3M Copper ≤ 3.7 µg/L ENRR1: AGM ≤ 2.9 Estuary 3M Nutrients (Chlorophyll-a) µg/L

< 21 days of beach Beach 3M Bacteria (Beach Advisories) advisories

Estuary 3M Copper ≤ 3.7 µg/L

ENRR2: PCT ≤ 10.2 Estuary 3M Nutrients (Chlorophyll-a) µg/L

ENRR2: AGM ≤ 0.049 Estuary 3M Nutrients (Total Phosphorus) mg/L

Estuary 3M Copper > 3.7 mg/L

Estuary 3M Copper ≤ 3.7 µg/L

Estuary 3M Copper ≤ 3.7 µg/L

Estuary 3M Copper ≤ 3.7 µg/L

Estuary 3M Copper ≤ 3.7 µg/L

Estuary 3M Copper ≤ 3.7 µg/L ENRH5: AGM ≤ 1.7 µg/L Estuary 3M Nutrients (Chlorophyll-a) ENRH9: AGM ≤ 1.1 µg/L AGM ≤ 11 µg/L

ENRH5: AGM ≤ 1.7 Estuary 3M Nutrients (Chlorophyll-a) µg/L AGM ≤ 11 µg/L

ENRH5: AGM ≤ 0.30 Estuary 3M Nutrients (Total Nitrogen) mg/L

ENRH9: AGM ≤ 1.1 Estuary 3M Nutrients (Chlorophyll-a) µg/L

Estuary 3M Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform > 400 counts per 100ml

Estuary 3M Copper ≤ 3.7 µg/L

Stream 3F Nutrients Nutrients (Chlorophyll-a) ≤ 20 µg/L Stream 3F Turbidity Turbidity ≤ 29 NTU + background

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Pb ≤ e^(1.273[lnH]- Stream 3F Lead 4.705)

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Dissolved Oxygen Total Phosphorus ≥ 5.0 mg/L

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Stream 3F Nutrients (Total Phosphorus) AGM ≤ 0.12 mg/L

RPS ≤ 25%, or when between 20% - 25% Stream 3F Nutrients (Algal Mats) Evaluation of Algal Autoecological Data Indicates No Imbalance

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Nutrients (added from Stream 3F Dissolved Oxygen < 5.0 mg/l comments) LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Biochemical Lake 3F Dissolved Oxygen Total Nitrogen ≥ 5.0 mg/L Oxygen Demand

Lake 3F Dissolved Oxygen Dissolved Oxygen Total Nitrogen ≥ 5.0 mg/L

Biochemical Stream 3F Dissolved Oxygen Total Nitrogen ≥ 5.0 mg/L Oxygen Demand

Stream 3F Dissolved Oxygen Dissolved Oxygen Total Nitrogen ≥ 5.0 mg/L

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Dissolved Oxygen (Percent Stream 3F Dissolved Oxygen Nutrients ≥ 38 % Saturation)

LVS C of C ≥ 2.5 and Stream 3F Nutrients Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Stream 3F Nutrients Nutrients (Total Nitrogen) AGM ≤ 1.54 mg/L

Nutrients (added from Stream 3F Dissolved Oxygen Dissolved Oxygen < 5.0 mg/l comments)

Median TN = 1.9545 Stream 3F Nutrients Nutrients (Chlorophyll-a) µg/L Nutrients (added from Stream 3F Dissolved Oxygen Dissolved Oxygen < 5.0 mg/l comments)

Stream 3F Un-ionized Ammonia ≤ 0.02 mg/L as NH3

> 400 colonies per 100 Estuary 3M Fecal Coliform mL

Estuary 3M Iron ≤ 0.3 mg/L

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

> 400 colonies per 100 Stream 3F Fecal Coliform mL

Estuary 3M Iron ≤ 0.3 mg/L

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

> 400 colonies per 100 Estuary 3M Fecal Coliform mL > 400 colonies per 100 Estuary 3M Fecal Coliform mL > 400 colonies per 100 Stream 3F Fecal Coliform mL > 400 colonies per 100 Stream 3F Fecal Coliform mL > 400 colonies per 100 Estuary 3M Fecal Coliform mL

Estuary 3M Iron ≤ 0.3 mg/L

> 400 colonies per 100 Stream 3F Fecal Coliform mL > 400 colonies per 100 Stream 3F Fecal Coliform mL > 400 colonies per 100 Stream 3F Fecal Coliform mL > 400 colonies per 100 Stream 3F Fecal Coliform mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Median TN = 1.016 Stream 3F Nutrients (Chlorophyll-a) mg/L Median TP = 0.053 mg/L

Nutrients (added from Stream 3F Dissolved Oxygen Dissolved Oxygen < 5.0 mg/l comments) Median TN = 2.0045 Stream 3F Nutrients Nutrients (Chlorophyll-a) µg/L

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Lake 3F Fecal Coliform ≤ 400 Counts / 100 mL

Lake 1 Fecal Coliform ≤ 400 Counts / 100 mL

Lake 3F Fecal Coliform ≤ 400 Counts / 100 mL

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Total Nitrogen, Biochemical Stream 3F Dissolved Oxygen Dissolved Oxygen ≥ 5.0 mg/L Oxygen Demand

Stream 3F Nutrients Nutrients (Chlorophyll-a) ≤ 20 µg/L

LVS C of C ≥ 2.5 and Stream 3F Nutrients Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Stream 3F Nutrients Nutrients (Total Nitrogen) AGM ≤ 1.54 mg/L

Nutrients (added from Stream 3F Dissolved Oxygen Dissolved Oxygen < 5.0 mg/l comments) Stream 3F Nutrients Nutrients (Chlorophyll-a) ≤ 20 µg/L

Nutrients (added from Stream 3F Dissolved Oxygen Dissolved Oxygen < 5.0 mg/l comments)

Nutrients (added from Stream 3F Dissolved Oxygen Dissolved Oxygen < 5.0 mg/l comments)

Nutrients (added from Stream 3F Dissolved Oxygen Dissolved Oxygen < 5.0 mg/l comments)

Stream 3F Fecal Coliform > 400 colonies/100 ml

Stream 3F Fecal Coliform > 400 colonies/100 ml

Nutrients (added from Stream 3F Dissolved Oxygen Dissolved Oxygen < 5.0 mg/l comments)

Nutrients (added from Stream 3F Dissolved Oxygen Dissolved Oxygen < 5.0 mg/l comments)

Average score of at least two temporally Lake 3F Biology Nutrients independent LVI scores ≥ 43.

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.16 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.05 mg/L

ENRD10: AAM ≤ 0.63 Estuary 2 Nutrients (Total Nitrogen) mg/L

Estuary 3M Iron ≤ 0.3 mg/L

Estuary 3M Copper ≤ 3.7 µg/L

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

LVS C of C ≥ 2.5 and Stream 3F Nutrients (Macrophytes) LVS FLEPPC ≤ 25%

Estuary 3M Iron ≤ 0.3 mg/L

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

Stream 3F Iron ≤ 1.0 mg/L

Estuary 3M Iron ≤ 0.3 mg/L

Estuary 3M Copper ≤ 3.7 µg/L

Estuary 3M Enterococci ≤ 130 Counts / 100 mL Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Estuary 3M Iron ≤ 0.3 mg/L

Estuary 3M Copper ≤ 3.7 µg/L

Dissolved Oxygen (Percent Estuary 3M Nutrients ≥ 42 % Saturation)

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

ENRD10: AAM ≤ 0.63 Estuary 3M Nutrients (Total Nitrogen) mg/L

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Total Nitrogen, Total Estuary 3M Dissolved Oxygen Dissolved Oxygen ≥ 4.0 mg/L Phosphorus

Estuary 3M Iron ≤ 0.3 mg/L

Estuary 3M Copper ≤ 3.7 µg/L

Estuary 3M Enterococci ≤ 130 Counts / 100 mL ENRD10: AAM ≤ 0.63 Estuary 3M Nutrients (Total Nitrogen) mg/L

ENRD10: AAM ≤ 0.63 Estuary 3M Nutrients (Total Nitrogen) mg/L

AGM ≤ 11 µg/L ENRD11: AGM ≤ 5.9 µg/L Estuary 2 Nutrients (Chlorophyll-a) ENRD12: AGM ≤ 5.8 µg/L ENRE1: AGM ≤ 5.8 µg/L

ENRD11: AGM ≤ 0.63 mg/L ENRD12: AGM ≤ 0.47 Estuary 2 Nutrients (Total Nitrogen) mg/L ENRE1: AGM ≤ 0.47 mg/L Stream 3F Iron ≤ 1.0 mg/L

Exceeds Shellfish Fecal Coliform (SEAS Evaluation & Estuary 2 Classification) Assessment Section (SEAS) thresholds

Estuary 2 Fecal Coliform (3) ≤ 14 MPN/100 mL

Nutrients (added from Stream 3F Dissolved Oxygen Dissolved Oxygen ≥ 5.0 mg/L comments)

Stream 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Average score of at least two temporally Lake 3F Biology Nutrients independent LVI scores ≥ 43.

Lake 3F Nutrients Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.16 mg/L; If Chl-a has Insufficient Lake 3F Nutrients Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.05 mg/L

Stream 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L Stream 3F Nutrients Nutrients (Chlorophyll-a) ≤ 20 µg/L

Stream 3F Nutrients Nutrients (Chlorophyll-a) ≤ 20 µg/L

Median TN = 0.95 mg/L Stream 3F Nutrients Nutrients (Chlorophyll-a) Median TP = 0.1595 mg/L

Biochemical Oxygen Stream 3F Dissolved Oxygen Dissolved Oxygen ≥ 5.0 mg/L Demand

Nutrients (added from Stream 3F Dissolved Oxygen < 5.0 mg/l comments)

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

TN = 1.62 mg/L; TP = Estuary 3M Nutrients (Chlorophyll-a) 0.11 mg/L

Estuary 3M Copper ≤ 3.7 µg/L

Estuary 3M Copper ≤ 3.7 µg/L

Stream 3F Iron ≤ 1.0 mg/L

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

ENRE3: AGM ≤ 0.30 Estuary 2 Nutrients (Total Nitrogen) mg/L

Exceeds Shellfish Fecal Coliform (SEAS Environmental Estuary 2 Classification) Assessment Section (SEAS) thresholds

ENRE3: AGM ≤ 0.30 Estuary 2 Nutrients (Total Nitrogen) mg/L ENRE3: AGM ≤ 0.046 Estuary 2 Nutrients (Total Phosphorus) mg/L

Estuary 2 Copper ≤ 3.7 µg/L

ENRD13: PCT ≤ 0.040 Estuary 2 Nutrients (Total Phosphorus) mg/L

Estuary 3M Copper ≤ 3.7 µg/L

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

Estuary 3M Copper ≤ 3.7 µg/L

Estuary 3M Iron ≤ 0.3 mg/L

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

Estuary 2 Copper Copper ≤ 3.7 µg/L

Estuary 2 Iron ≤ 0.3 mg/L

Estuary 2 Fecal Coliform ≤ 43 MPN/100 mL

Estuary 2 Fecal Coliform (3) ≤ 14 MPN/100 mL

ENRE4: AGM ≤ 4.3 Estuary 2 Nutrients (Chlorophyll-a) µg/L Estuary 3M Copper Copper ≤ 3.7 µg/L

Estuary 3M Iron ≤ 0.3 mg/L

Dissolved Oxygen (Percent Estuary 3M Nutrients ≥ 42 % Saturation)

Estuary 3M Enterococci ≤ 130 Counts / 100 mL

AGM ≤ 11 µg/L Estuary 3M Nutrients (Chlorophyll-a) ENRE4: AGM ≤ 4.3 µg/L

ENRE4: AGM ≤ 0.57 Estuary 3M Nutrients (Total Nitrogen) mg/L

ENRE4: AGM ≤ 0.045 Estuary 3M Nutrients (Total Phosphorus) mg/L

Nutrients (added from Stream 3F Dissolved Oxygen < 5.0 mg/L comments)

Estuary 2 Fecal Coliform > 400 Counts/100 ml Stream 3F Iron ≤ 1.0 mg/L

Estuary 3M Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform > 400 counts per 100ml

Shall not be increased more than 50% above Stream 3F Specific Conductance background or to 1275 μmhos/cm, whichever is greater.

Estuary 3M Copper > 3.7 µg/L

Estuary 3M Copper ≤ 3.7 µg/L

Estuary 3M Dioxin (in fish tissue)

Stream 3F Fecal Coliform > 400 counts per 100ml

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Shall not be increased more than 50% above Stream 3F Specific Conductance background or to 1275 μmhos/cm, whichever is greater.

Shall not be increased more than 50% above Stream 3F Specific Conductance background or to 1275 μmhos/cm, whichever is greater.

Shall not be increased more than 50% above Stream 3F Specific Conductance background or to 1275 μmhos/cm, whichever is greater.

Biochemical Oxygen Stream 3F Dissolved Oxygen Demand (added from < 5.0 mg/L comments) Balanced natural Lake 3F Nutrients (Other Information) population of flora and fauna.

Pb ≤ e(1.273[lnH]- Stream 3F Lead 4.705) µg/L

Spring 3F Nutrients (Nitrate-Nitrite) ≤ 0.35 mg/L

Biochemical Oxygen Stream 3F Dissolved Oxygen Demand (added from < 5.0 mg/L comments)

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Lead > e(1.273[LnH]-4.705)

Exceeds SEAS Estuary 3M Bacteria (in Shellfish) thresholds

Coastal 2 Fecal Coliform (3) ≤ 14 MPN / 100 mL

Coastal 2 Iron ≤ 0.3 mg/L Estuary 2 Fecal Coliform ≤ 43 MPN/100 mL

Estuary 2 Fecal Coliform (3) ≤ 14 MPN/100 mL

Exceeds Shellfish Fecal Coliform (SEAS Environmental Estuary 2 Classification) Assessment Section (SEAS) thresholds

Estuary 2 Iron ≤ 0.3 mg/L

Nutrients, Biochemical Stream 3F Dissolved Oxygen Dissolved Oxygen Oxygen Demand (added < 5.0 mg/L from comments)

Shall not be increased Stream 3F Specific Conductance above 1275 µmhos/cm

see 62-302.530(3), Stream 3F Total Ammonia F.A.C.

Spring 3F Nutrients (Nitrate-Nitrite) ≤ 0.35 mg/L

Nutrients, Biochemical Lake 3F Dissolved Oxygen Oxygen Demand (added < 5.0 mg/L from comments)

Stream 3F Fecal Coliform > 400 counts per 100ml

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 2 Fecal Coliform > 400 Counts/100 ml Biochemical Oxygen Stream 3F Dissolved Oxygen ≥ 5.0 mg/L Demand

Nutrients, Biochemical Stream 3F Dissolved Oxygen Oxygen Demand (added < 5.0 mg/L from comments)

Stream 3F Fecal Coliform > 400 Counts/100 ml Stream 3F Coliforms Fecal Coliform > 400 Counts/100 ml

Nutrients (added from Stream 3F Dissolved Oxygen Dissolved Oxygen < 5.0 mg/L comments)

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Iron ≤ 1.0 mg/L

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL Estuary 2 Fecal Coliform ≤ 43 MPN/100 mL

Estuary 2 Fecal Coliform (3) ≤ 14 MPN / 100 mL

Exceeds Shellfish Fecal Coliform (SEAS Evaluation & Estuary 2 Classification) Assessment Section (SEAS) thresholds

Estuary 2 Fecal Coliform ≤ 43 MPN/100 mL

ENRV2: AGM ≤ 0.69 Estuary 2 Nutrients (Total Nitrogen) mg/L

Spring 3F Nutrients (Nitrate-Nitrite) ≤ 0.35 mg/L

Exceeds Shellfish Fecal Coliform (SEAS Environmental Estuary 2 Classification) Assessment Section (SEAS) thresholds

Exceeds Shellfish Fecal Coliform (SEAS Environmental Estuary 2 Classification) Assessment Section (SEAS) thresholds

Estuary 2 Fecal Coliform (3) ≤ 14 MPN / 100 mL

Exceeds Shellfish Fecal Coliform (SEAS Evaluation & Estuary 2 Classification) Assessment Section (SEAS) thresholds

Estuary 2 Fecal Coliform ≤ 43 MPN/100 mL

Exceeds Shellfish Fecal Coliform (SEAS Evaluation & Estuary 2 Classification) Assessment Section (SEAS) thresholds

Estuary 2 Fecal Coliform (3) ≤ 14 MPN / 100 mL Exceeds Shellfish Fecal Coliform (SEAS Evaluation & Estuary 2 Classification) Assessment Section (SEAS) thresholds

Nutrients, Biochemical Lake 3F Dissolved Oxygen Oxygen Demand (added < 5.0 mg/L from comments)

Average score of at least two temporally independent SCI scores ≥ 40; or either of the two most recent Stream 3F Biology Nutrients SCI scores ≥ 35; or if there are only two SCI scores and there is less than or equal to a 20 point difference.

Stream 3F Nutrients (Total Nitrogen) AGM ≤ 0.67 mg/L

Pb ≤ e(1.273[lnH]- Stream 3F Lead 4.705) µg/L

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Coliforms Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Iron ≤ 1.0 mg/L

Stream 3F Coliforms Fecal Coliform > 400 Counts/100 ml Total Nitrogen, Biochemical Stream 3F Dissolved Oxygen ≥ 5.0 mg/L Oxygen Demand

Average score of at least two temporally independent SCI scores ≥ 40; or either of the two most recent Stream 3F Biology Nutrients, Dissolved Oxygen SCI scores ≥ 35; or if there are only two SCI scores and there is less than or equal to a 20 point difference.

Stream 3F Nutrients (Total Nitrogen) AGM ≤ 1.03 mg/L

Stream 3F Nutrients (Total Phosphorus) AGM ≤ 0.18 mg/L

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Iron ≤ 1.0 mg/L

Stream 3F Iron ≤ 1.0 mg/L

Stream 3F Iron ≤ 1.0 mg/L < 21 days of beach Beach 3M Bacteria (Beach Advisories) advisories

< 21 days of beach Beach 3M Bacteria (Beach Advisories) advisories

Estuary 2 Copper ≤ 3.7 µg/L

Exceeds Shellfish Fecal Coliform (SEAS Evaluation & Estuary 2 Classification) Assessment Section (SEAS) thresholds

Exceeds Shellfish Bacteria (Shellfish Evaluation & Estuary 2 Harvesting Classification) Assessment Section (SEAS) thresholds

Estuary 2 Iron ≤ 0.3 mg/L

Exceeds Shellfish Bacteria (Shellfish Evaluation & Estuary 2 Harvesting Classification) Assessment Section (SEAS) thresholds

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Average score of at least two temporally independent SCI scores ≥ 40; or either of the two most recent Stream 3F Biology Nutrients SCI scores ≥ 35; or if there are only two SCI scores and there is less than or equal to a 20 point difference.

Stream 3F Nutrients (Total Nitrogen) AGM ≤ 0.67 mg/L RPS ≤ 25%, or when between 20% - 25% Stream 3F Nutrients (Algal Mats) Evaluation of Algal Autoecological Data Indicates No Imbalance

Stream 3F Nutrients (Total Nitrogen) AGM ≤ 0.67 mg/L

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Iron ≤ 1.0 mg/L

Stream 3F Iron ≤ 1.0 mg/L

Lake 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform > 400 colonies/100 ml

Lake 3F Nutrients (Chlorophyll-a) ≤ 6 µg/L

Chl-a AGM ≤ 6 µg/L, TN AGM ≤ 0.93 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TN AGM ≤ 0.51 mg/L

Chl-a AGM ≤ 6 µg/L, TP AGM ≤ 0.03 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TP AGM ≤ 0.01 mg/L

Estuary 3M Enterococci ≤ 130 Counts / 100 mL Exceeds Shellfish Bacteria (Shellfish Evaluation & Estuary 2 Harvesting Classification) Assessment Section (SEAS) thresholds

Exceeds Shellfish Bacteria (Shellfish Evaluation & Estuary 2 Coliforms Harvesting Classification) Assessment Section (SEAS) thresholds Exceeds Shellfish Bacteria (Shellfish Evaluation & Estuary 2 Coliforms Harvesting Classification) Assessment Section (SEAS) thresholds

ENRL4: AGM ≤ 3.9 Estuary 3M Nutrients (Chlorophyll-a) µg/L

< 21 days of beach Coastal 3M Bacteria (Beach Advisories) advisories

Exceeds Shellfish Bacteria (Shellfish Evaluation & Estuary 2 Harvesting Classification) Assessment Section (SEAS) thresholds

Estuary 2 Fecal Coliform ≤ 43 MPN / 100 mL

Exceeds Shellfish Bacteria (Shellfish Evaluation & Estuary 2 Harvesting Classification) Assessment Section (SEAS) thresholds

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L Average score of at least two temporally independent LVI scores ≥ 43; or either of the two most recent LVI Lake 3F Biology Nutrients scores ≥ 43; or if there are only two LVI scores and there is less than or equal to a 20 point difference.

Lake 3F Nutrients (Chlorophyll-a) ≤ 6 µg/L

Chl-a AGM ≤ 6 µg/L, TN AGM ≤ 0.93 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TN AGM ≤ 0.51 mg/L

Chl-a AGM ≤ 6 µg/L, TP AGM ≤ 0.03 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TP AGM ≤ 0.01 mg/L

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Average score of at least two temporally independent SCI scores ≥ 40; or either of the two most recent Stream 3F Biology Nutrients, Dissolved Oxygen SCI scores ≥ 35; or if there are only two SCI scores and there is less than or equal to a 20 point difference. Dissolved Oxygen (Percent Stream 3F Nutrients ≥ 67 % Saturation)

RPS ≤ 25%, or when between 20% - 25% Stream 3F Nutrients (Algal Mats) Evaluation of Algal Autoecological Data Indicates No Imbalance

Stream 3F Nutrients (Total Phosphorus) AGM ≤ 0.18 mg/L

RPS ≤ 25%, or when between 20% - 25% Stream 3F Nutrients (Algal Mats) Evaluation of Algal Autoecological Data Indicates No Imbalance

ENRH3: AGM ≤ 0.5 µg/L ENRH4: AGM ≤ 0.7 µg/L ENRH6: AGM ≤ 0.4 µg/L Estuary 3M Nutrients (Chlorophyll-a) ENRH7: AGM ≤ 0.2 µg/L ENRH8: AGM ≤ 0.2 µg/L AGM ≤ 11 µg/L

Coastal 3M Copper > 3.7 µg/L

Coastal 3M Copper > 3.7 µg/L

Coastal 3M Copper > 3.7 µg/L Coastal 3M Copper > 3.7 µg/L Coastal 3M Copper > 3.7 µg/L Coastal 3M Copper > 3.7 µg/L Coastal 3M Copper > 3.7 µg/L Coastal 3M Copper > 3.7 µg/L Coastal 3M Copper ≤ 3.7 µg/L

Coastal 3M Copper > 3.7 µg/L

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Pb ≤ e(1.273[lnH]- Stream 3F Lead 4.705) µg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 6 µg/L

Chl-a AGM ≤ 6 µg/L, TN AGM ≤ 0.93 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TN AGM ≤ 0.51 mg/L

Chl-a AGM ≤ 6 µg/L, TP AGM ≤ 0.03 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TP AGM ≤ 0.01 mg/L

Lake 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.09 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.03 mg/L

Stream 2 Fecal Coliform ≤ 43 MPN / 100 mL

Stream 3F Fecal Coliform > 400 Counts/100 ml

Stream 3F Fecal Coliform > 400 Counts/100 ml

ENRM3: AGM ≤ 3.0 Estuary 3M Nutrients (Chlorophyll-a) µg/L ENRM3: AGM ≤ 0.33 Estuary 3M Nutrients (Total Nitrogen) mg/L

< 21 days of beach Beach 3M Bacteria (Beach Advisories) advisories

Exceeds Shellfish Bacteria (Shellfish Evaluation & Estuary 2 Harvesting Classification) Assessment Section (SEAS) thresholds

Estuary 2 Enterococci ≤ 130 Counts / 100 mL

Stream 2 Fecal Coliform ≤ 43 MPN / 100 mL

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Estuary 2 Fecal Coliform ≤ 43 MPN / 100 mL

< 21 days of beach Coastal 3M Bacteria (Beach Advisories) advisories

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

ENRM1: AGM ≤ 4.0 Estuary 3M Nutrients (Chlorophyll-a) µg/L

< 21 days of beach Coastal 3M Bacteria (Beach Advisories) advisories

Stream 2 Fecal Coliform ≤ 43 MPN / 100 mL Stream 3F Iron ≤ 1.0 mg/L

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Estuary 2 Fecal Coliform ≤ 43 MPN / 100 mL

< 21 days of beach Beach 3M Bacteria (Beach Advisories) advisories

Lake 3F Nutrients (Chlorophyll-a) ≤ 6 µg/L

Chl-a AGM ≤ 6 µg/L, TN AGM ≤ 0.93 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TN AGM ≤ 0.51 mg/L

Chl-a AGM ≤ 6 µg/L, TP AGM ≤ 0.03 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 6 µg/L, TP AGM ≤ 0.01 mg/L

Stream 3F Coliforms Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Exceeds SEAS Estuary 2 Bacteria (in Shellfish) thresholds

Estuary 2 Fecal Coliform ≤ 43 MPN / 100 mL

ENRM9: AGM ≤ 0.54 Estuary 2 Nutrients (Total Nitrogen) mg/L

ENRM9: AGM ≤ 0.049 Estuary 2 Nutrients (Total Phosphorus) mg/L

< 21 days of beach Beach 2 Bacteria (Beach Advisories) advisories

< 21 days of beach Coastal 3M Bacteria (Beach Advisories) advisories

< 21 days of beach Beach 3M Bacteria (Beach Advisories) advisories

Exceeds Shellfish Bacteria (Shellfish Evaluation & Estuary 2 Coliforms Harvesting Classification) Assessment Section (SEAS) thresholds ENRM7: AGM ≤ 3.1 Estuary 2 Nutrients (Chlorophyll-a) µg/L

ENRM7: AGM ≤ 0.36 Estuary 2 Nutrients (Total Nitrogen) mg/L

Exceeds Shellfish Bacteria (Shellfish Evaluation & Estuary 2 Coliforms Harvesting Classification) Assessment Section (SEAS) thresholds

Estuary 2 Coliforms Fecal Coliform (3) ≤ 14 MPN / 100 mL

ENRM7: AGM ≤ 0.36 Estuary 2 Nutrients (Total Nitrogen) mg/L

< 21 days of beach Beach 2 Bacteria (Beach Advisories) advisories

Dissolved Oxygen (Percent Estuary 2 Dissolved Oxygen Nutrients ≥ 42 % Saturation)

ENRM4: AGM ≤ 4.4 Estuary 2 Nutrients Nutrients (Chlorophyll-a) µg/L ENRM4: AGM ≤ 0.46 Estuary 2 Nutrients Nutrients (Total Nitrogen) mg/L

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 2.23 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.27 mg/L

Chl-a AGM ≤ 20 µg/L, TP AGM ≤ 0.16 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Phosphorus) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TP AGM ≤ 0.05 mg/L

Dissolved Oxygen (Percent Lake 3F Nutrients ≥ 67 % Saturation)

Chl-a AGM ≤ 20 µg/L, TN AGM ≤ 2.23 mg/L; If Chl-a has Insufficient Lake 3F Nutrients (Total Nitrogen) or No Data to calculate AGM or if Chl-a AGM > 20 µg/L, TN AGM ≤ 1.27 mg/L

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Estuary 2 Coliforms Fecal Coliform (3) ≤ 14 MPN / 100 mL

Estuary 2 Fecal Coliform ≤ 43 MPN/100 mL

RPS ≤ 25%, or when between 20% - 25% Stream 3F Nutrients (Algal Mats) Evaluation of Algal Autoecological Data Indicates No Imbalance

Estuary 3M Enterococci ≤ 130 Counts / 100 mL Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

< 21 days of beach Beach 3M Bacteria (Beach Advisories) advisories

< 21 days of beach Beach 3M Bacteria (Beach Advisories) advisories

< 21 days of beach Beach 3M Bacteria (Beach Advisories) advisories

< 21 days of beach Beach 3M Bacteria (Beach Advisories) advisories

< 21 days of beach Beach 3M Bacteria (Beach Advisories) advisories

< 21 days of beach Beach 3M Bacteria (Beach Advisories) advisories

< 21 days of beach Beach 3M Bacteria (Beach Advisories) advisories < 21 days of beach Beach 3M Bacteria (Beach Advisories) advisories

< 21 days of beach Coastal 3M Bacteria (Beach Advisories) advisories

< 21 days of beach Beach 3M Bacteria (Beach Advisories) advisories

< 21 days of beach Coastal 3M Bacteria (Beach Advisories) advisories

< 21 days of beach Beach 3M Bacteria (Beach Advisories) advisories

< 21 days of beach Beach 3M Bacteria (Beach Advisories) advisories

< 21 days of beach Beach 3M Bacteria (Beach Advisories) advisories

< 21 days of beach Beach 3M Bacteria (Beach Advisories) advisories < 21 days of beach Beach 3M Bacteria (Beach Advisories) advisories

< 21 days of beach Beach 3M Bacteria (Beach Advisories) advisories

Exceeds Shellfish Fecal Coliform (SEAS Evaluation & Coastal 2 Classification) Assessment Section (SEAS) thresholds

< 21 days of beach Beach 3M Bacteria (Beach Advisories) advisories

< 21 days of beach Beach 3M Bacteria (Beach Advisories) advisories

Exceeds Shellfish Fecal Coliform (SEAS Evaluation & Coastal 2 Classification) Assessment Section (SEAS) thresholds

ENRX13: AGM ≤ 0.45 Coastal 3M Nutrients (Total Nitrogen) mg/L

ENRX13: AGM ≤ 0.45 Coastal 3M Nutrients (Total Nitrogen) mg/L

Exceeds Shellfish Fecal Coliform (SEAS Evaluation & Coastal 2 Classification) Assessment Section (SEAS) thresholds ENRX13: AGM ≤ 3.3 µg/L Coastal 2 Nutrients (Chlorophyll-a) ENRX14: AGM ≤ 3.3 µg/L ENRX13: AGM ≤ 0.45 mg/L Coastal 2 Nutrients (Total Nitrogen) ENRX14: AGM ≤ 0.45 mg/L ENRX13: AGM ≤ 0.021 mg/L Coastal 2 Nutrients (Total Phosphorus) ENRX14: AGM ≤ 0.021 mg/L

Exceeds Shellfish Fecal Coliform (SEAS Evaluation & Coastal 2 Classification) Assessment Section (SEAS) thresholds

Exceeds SEAS Coastal 3M Bacteria (in Shellfish) thresholds

Coastal 2 Fecal Coliform (3) ≤ 14 MPN/100 mL

Exceeds Shellfish Fecal Coliform (SEAS Evaluation & Coastal 2 Classification) Assessment Section (SEAS) thresholds

ENRV3 Coastal 2 Nutrients (Chlorophyll-a) AGM ≤ 4.9 µg/L

ENRV3 AGM ≤ -0.0328*AASal Coastal 2 Nutrients (Total Nitrogen) + 1.4177

Exceeds Shellfish Bacteria (Shellfish Evaluation & Coastal 2 Harvesting Classification) Assessment Section (SEAS) thresholds

Coastal 2 Fecal Coliform (3) ≤ 14 MPN / 100 mL

Exceeds Shellfish Bacteria (Shellfish Evaluation & Coastal 2 Harvesting Classification) Assessment Section (SEAS) thresholds

ENRW3 Coastal 3M Nutrients (Chlorophyll-a) AGM ≤ 0.8 µg/L

ENRW3 Coastal 3M Nutrients (Total Nitrogen) AGM ≤ 0.45 mg/L < 21 days of beach Coastal 3M Bacteria (Beach Advisories) advisories

ENRW11 Coastal 3M Nutrients (Total Nitrogen) AGM ≤ 0.47 mg/L

< 21 days of beach Beach 3M Bacteria (Beach Advisories) advisories

ENRE2: AGM ≤ 0.25 Coastal 3M Nutrients (Total Nitrogen) mg/L

ENRE2: AGM ≤ 0.25 Coastal 2 Nutrients (Total Nitrogen) mg/L

Coastal 3M Bacteria (in Shellfish)

Stream 3F Nutrients (Chlorophyll-a) ≤ 20 µg/L

Pb ≤ e(1.273[lnH]- Stream 3F Lead 4.705) µg/L

ENRG1 AGM ≤ 0.25 mg/L ENRG2 AGM ≤ 0.23 mg/L ENRG3 Coastal 3M Nutrients (Total Nitrogen) AGM ≤ 0.21 mg/L ENRG4 AGM ≤ 0.21 mg/L ENRG6 AGM ≤ 0.17 mg/L

< 21 days of beach Beach 3M Bacteria (Beach Advisories) advisories < 21 days of beach Beach 3M Bacteria (Beach Advisories) advisories < 21 days of beach Beach 3M Bacteria (Beach Advisories) advisories ENRG3 AGM ≤ 0.21 mg/L Coastal 3M Nutrients (Total Nitrogen) ENRG6 AGM ≤ 0.17 mg/L

Pb ≤ e(1.273[lnH]- Lake 3F Lead 4.705) µg/L

Pb ≤ e^(1.273[lnH]- Stream 3F Lead 4.705)

Biochemical Oxygen Stream 3F Dissolved Oxygen Demand (added from < 5.0 mg/L comments)

ENRG3 AGM ≤ 0.21 mg/L Coastal 3M Nutrients (Total Nitrogen) ENRG6 AGM ≤ 0.17 mg/L

< 21 days of beach Beach 3M Bacteria (Beach Advisories) advisories

< 21 days of beach Beach 3M Bacteria (Beach Advisories) advisories

ENRG6: AGM ≤ 0.17 mg/L Coastal 3M Nutrients (Total Nitrogen) ENRG7: AGM ≤ 0.18 mg/L

Stream 3F Fecal Coliform > 400 Counts/100 ml

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Exceeds Shellfish Bacteria (Shellfish Evaluation & Estuary 2 Harvesting Classification) Assessment Section (SEAS) thresholds < 21 days of beach Coastal 3M Bacteria (Beach Advisories) advisories

Estuary 3M Fecal Coliform ≤ 400 Counts / 100 mL

Pb ≤ e(1.273[lnH]- Lake 3F Lead 4.705) µg/L Pb ≤ e(1.273[lnH]- Lake 3F Lead 4.705) µg/L

Biochemical Oxygen Stream 3F Dissolved Oxygen Demand (added from < 5.0 mg/L comments)

Estuary 2 Fecal Coliform ≤ 43 MPN / 100 mL

Estuary 2 Fecal Coliform (3) ≤ 14 MPN / 100 mL

Stream 3F Fecal Coliform ≤ 400 Counts / 100 mL

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Stream 3F Fecal Coliform > 400 Counts/100 ml

Estuary 2 Fecal Coliform (3) ≤ 14 MPN / 100 mL

< 21 days of beach Coastal 3M Bacteria (Beach Advisories) advisories < 21 days of beach Coastal 3M Bacteria (Beach Advisories) advisories < 21 days of beach Coastal 3M Bacteria (Beach Advisories) advisories

Stream 3F Coliforms Fecal Coliform > 400 Counts/100 ml

Estuary 2 Fecal Coliform ≤ 43 MPN / 100 mL

Stream 3F Fecal Coliform > 400 Counts/100 ml

Stream 3F Escherichia coli ≤ 410 Counts / 100 mL

Estuary 2 Fecal Coliform ≤ 43 MPN / 100 mL

Stream 3F Iron ≤ 1.0 mg/L

DOH Fish Tissue Stream 3F Arsenic (in fish tissue) Action Level For Recreational Fishermen Stream 3F Fecal Coliform > 400 Counts/100 ml

ults represents a single sample for the purpose of determining n. mpairment h have been assigned a “low” priority. t 5 years, within the next 10 years. represents the number of exceedances and y represents the total number of samples. represents the number of exceedances and y represents the total number of samples. Projected Year For Priority for TMDL Verified Period TMDL Development3 Assessment Data8 Development3

Low 5/23

High Impaired

ENRN4: AGM 2008 (0.33 mg/L) 2009 (0.41 mg/L) 2010 (0.34 mg/L) Medium 2011 (0.31 mg/L) 2012 (0.41 mg/L) 2013 (0.40 mg/L) 2014 (0.30 mg/L) 2015 (0.30 mg/L)

Low vp=150/532

Medium 2009

Medium 2009

ENRN3: AGM 2008 (0.35 mg/L) 2009 (0.42 mg/L) 2010 (0.37 mg/L) Medium 2011 (0.30 mg/L) 2012 (0.33 mg/L) 2013 (0.36 mg/L) 2014 (0.26 mg/L)

Medium 2009

Medium 2009

ENRN1: AGM 2008 (0.34 mg/L) 2009 (0.31 mg/L) Medium 2010 (0.26 mg/L) 2011 (0.27 mg/L) 2012 (0.44 mg/L) 2014 (0.47 mg/L)

Medium 2009

Low N/A

ENRN2: AGM 2008 (0.31 mg/L) 2009 (0.27 mg/L) Medium 2010 (0.28 mg/L) 2011 (0.23 mg/L) 2012 (0.36 mg/L) 2014 (0.29 mg/L) High Impaired

ENRN2: AGM 2008 (0.31 mg/L) 2009 (0.26 mg/L) Medium 2010 (0.29 mg/L) 2011 (0.23 mg/L) 2012 (0.37 mg/L) 2014 (0.31 mg/L)

Low 5/25

Low vp=8/9

ENRX3 (PCT) Medium 8/29

ENRX3 (PCT) Medium 7/29

Low N/A

Low vp=6/12

Low 11/38

Low

Low vp=9/12

Low vp=19/20

Low vp=6/15

Low vp=6/8

Low vp=21/109

Low 9/10

Low vp=8/15

Medium vp=13/22

Low vp=5/6 Low NA

Low NA

Low vp=7/23

High NA

Low vp=7/22

High NA

High 2 / 15

High NA

Medium 2008

Medium 2008

High Impaired

ENRO1: AGM 2008 (0.44 mg/L) 2009 (0.41 mg/L) 2010 (0.44 mg/L) Medium 2011 (0.50 mg/L) 2012 (0.72 mg/L) 2013 (0.50 mg/L) 2014 (0.32 mg/L) Beach Advisories 2008 (0 days) 2009 (7 days) 2010 (6 days) High 2011 (13 days) 2012 (71 days) 2013 (0 days) 2014 (0 days) 2015 (20 days)

Medium 2009 Low N/A

Low N/A

Medium 2008

Low Impaired

Medium 12/12

Medium 2008

Medium 2008

Low 69/796

High NA

High NA

Low N/A

High NA

Low N/A

Low N/A

Low N/A Medium

Medium 2008

Medium 35/63

Medium

Medium 16/16

Medium 7/24

Medium 72/74

Medium 7/31

AGM 2011 (34 µg/L) 2012 (25 µg/L) 2013 (20 µg/L) High 2014 (5 µg/L) 2015 (30 µg/L) 2016 (25 µg/L) 2017 (29 µg/L) AGM 2011 (0.81 mg/L) 2012 (0.70 mg/L) 2013 (0.92 mg/L) High 2014 (0.71 mg/L) 2015 (0.71 mg/L) 2016 (0.76 mg/L) 2017 (0.76 mg/L) AGM 2011 (0.06 mg/L) 2012 (0.05 mg/L) 2013 (0.11 mg/L) High 2014 (0.05 mg/L) 2015 (0.05 mg/L) 2016 (0.06 mg/L) 2017 (0.05 mg/L) AGM 2011 (30 µg/L) 2012 (20 µg/L) 2013 (16 µg/L) High 2014 (2 µg/L) 2015 (32 µg/L) 2016 (28 µg/L) 2017 (23 µg/L) AGM 2011 (0.76 mg/L) 2012 (0.80 mg/L) 2013 (1.07 mg/L) High 2014 (0.81 mg/L) 2015 (0.85 mg/L) 2016 (0.97 mg/L) 2017 (0.82 mg/L)

AGM 2011 (0.06 mg/L) 2012 (0.07 mg/L) 2013 (0.11 mg/L) High 2014 (0.07 mg/L) 2015 (0.07 mg/L) 2016 (0.08 mg/L) 2017 (0.07 mg/L)

AGM 2011 (22 µg/L) 2012 (15 µg/L) 2013 (10 µg/L) High 2014 (2 µg/L) 2015 (22 µg/L) 2016 (17 µg/L) 2017 (27 µg/L) AGM 2011 (0.75 mg/L) 2012 (0.80 mg/L) 2013 (0.89 mg/L) High 2014 (0.80 mg/L) 2015 (0.79 mg/L) 2016 (0.85 mg/L) 2017 (0.75 mg/L)

AGM 2011 (0.07 mg/L) 2012 (0.06 mg/L) 2013 (0.11 mg/L) High 2014 (0.08 mg/L) 2015 (0.06 mg/L) 2016 (0.09 mg/L) 2017 (0.06 mg/L)

Medium

High 15/20

High 8/10 Medium 19/20

Medium 7/19

Low

High N/A

2003 (6.4 µg/L) 2004 (6.5 µg/L) 2005 (8.3 µg/L) Medium 2006 (11 µg/L) 2007 (11 µg/L) 2008 (11 µg/L) 2009 (34 µg/L)

Medium 13/67

5/29/2014: Avg CofC - 2.3, FLEPPC - 30% 11/20/2014: Avg CofC - Medium 2.4, FLEPPC - 29% 3/16/2016: Avg CofC - 1.8, FLEPPC - 34%

Medium N/A

AGM 2009 (0.61 mg/L) 2010 (0.58 mg/L) Medium 2011 (0.57 mg/L) 2012 (0.41 mg/L) 2013 (0.49 mg/L)

Medium No Data AGM 2009 (0.63 mg/L) 2010 (0.63 mg/L) 2011 (0.72 mg/L) Medium 2012 (0.76 mg/L) 2013 (0.72 mg/L) 2014 (0.89 mg/L) 2015 (0.50 mg/L)

Medium 36/164

AGM 2009 (0.15 mg/L) 2010 (0.28 mg/L) Medium 2011 (0.24 mg/L) 2012 (0.15 mg/L) 2013 (0.15 mg/L) 2014 (0.15 mg/L)

AGM 2014 (0.14 mg/L) Medium 2015 (0.18 mg/L) 2016 (0.14 mg/L)

High N/A

High N/A

AGM 2011 (0.27 mg/L) 2012 (0.45 mg/L) Medium 2013 (0.41 mg/L) 2014 (0.68 mg/L) 2015 (0.52 mg/L) AGM 2011 (0.40 mg/L) Medium 2013 (0.67 mg/L) 2014 (1.07 mg/L) 2015 (0.23 mg/L)

Low

Low

High N/A 3/11/2014: 61% Medium 2/16/2015: 29%

3/11/2014: Avg CofC - 2.1, FLEPPC - 36% Medium 2/16/2015: Avg CofC - 1.3, FLEPPC - 55%

Medium N/A

AGM 2009 (1.09 mg/L) 2010 (1.38 mg/L) Medium 2011 (1.40 mg/L) 2012 (1.30 mg/L) 2013 (1.22 mg/L)

Low N/A

Low 19/121

Low Impaired

High NA

Low N/A

Medium N/A AGM 2009 (0.61 mg/L) 2010 (1.49 mg/L) Medium 2011 (1.32 mg/L) 2012 (1.38 mg/L) 2013 (1.31 mg/L) AGM 2009 (0.17 mg/L) Medium 2010 (0.06 mg/L) 2011 (0.49 mg/L) 2013 (0.49 mg/L)

03/20/2012: 100% 11/16/2016: 21% Medium 11/21/2017: 24% 03/19/2018: 30%

9/23/2014: Avg CofC - 1.4, FLEPPC - 51% Medium 12/29/2014: Avg CofC - 1.9, FLEPPC - 46%

LVI (n=3) Big Mean (21) Medium Mean 1 (24), Mean 2 (22)

AGM 2010 (10 µg/L) Medium 2016 (28 µg/L) 2017 (25 µg/L)

AGM 2010 (1.00 mg/L) Medium 2016 (1.08 mg/L) 2017 (1.20 mg/L)

AGM 2010 (0.05 mg/L) Medium 2016 (0.05 mg/L) 2017 (0.06 mg/L)

Medium AGM Medium 2016 (7 µg/L) 2017 (7 µg/L)

AGM Medium 2016 (0.83 mg/L) 2017 (0.81 mg/L)

AGM Medium 2016 (0.02 mg/L) 2017 (0.02 mg/L)

High 2005

Medium N/A

Medium 15/53

Medium 23/38

High 48/92

11/04/2013: Avg CofC - 1.1, FLEPPC - 64% 03/27/2014: Avg CofC - High 1.3, FLEPPC - 44% 10/26/2015: Avg CofC - 2.0, FLEPPC - 40% (n=2)

Annual Geometric Mean(s) 2011 (45 µg/L) Medium 2012 (56 µg/L) 2013 (49 µg/L) 2014 (51 µg/L) Annual Geometric Mean(s) 2011 (2.09 mg/L) Medium 2012 (2.10 mg/L) 2013 (2.13 mg/L) 2014 (2.39 mg/L)

Annual Geometric Mean(s) 2011 (0.05 mg/L) Medium 2012 (0.07 mg/L) 2013 (0.06 mg/L) 2014 (0.05 mg/L)

Low 7/18

Low 8/23

Low 10/35

Annual Geometric Mean(s) 2007 (2.29 mg/L) 2008 (2.21 mg/L) Medium 2009 (2.27 mg/L) 2010 (2.18 mg/L) 2011 (2.26 mg/L) 2012 (2.27 mg/L) 2013 (2.32 mg/L) Annual Geometric Mean(s) Medium 2008 (1.21 mg/L) 2009 (1.34 mg/L)

Low

AGM 2015 (30 µg/L) Medium 2017 (22 µg/L) 2018 (29 µg/L)

Medium 15/23

AGM 2011 (64 µg/L) Medium 2013 (40 µg/L) 2014 (35 µg/L) AGM 2011 (20 µg/L) Medium 2015 (12 µg/L) 2016 (12 µg/L) 2017 (9 µg/L)

AGM 2011 (0.78 mg/L) Medium 2015 (0.71 mg/L) 2016 (0.71 mg/L) 2017 (0.62 mg/L)

AGM 2011 (0.02 mg/L) Medium 2015 (0.03 mg/L) 2016 (0.03 mg/L) 2017 (0.03 mg/L)

LVI (n=2) WBID Mean (34) Medium Mean 1 (33), Mean 2 (36)

AGM 2015 (13 µg/L) Medium 2016 (12 µg/L) 2017 (13 µg/L)

AGM 2015 (0.66 mg/L) Medium 2016 (0.72 mg/L) 2017 (0.74 mg/L)

AGM 2015 (0.02 mg/L) Medium 2016 (0.02 mg/L) 2017 (0.02 mg/L) LVI (n=3) Big Mean (31) Medium Mean 1 (24), Mean 2 (29)

AGM 2009 (5 µg/L) 2010 (11 µg/L) 2011 (11 µg/L) Medium 2012 (7 µg/L) 2013 (10 µg/L) 2014 (10 µg/L) 2015 (14 µg/L) AGM 2009 (0.54 mg/L) 2010 (0.70 mg/L) 2011 (0.76 mg/L) Medium 2012 (0.64 mg/L) 2013 (0.65 mg/L) 2014 (0.67 mg/L) 2015 (0.82 mg/L) AGM 2009 (0.03 mg/L) 2010 (0.04 mg/L) 2011 (0.05 mg/L) Medium 2012 (0.03 mg/L) 2013 (0.05 mg/L) 2014 (0.04 mg/L) 2015 (0.04 mg/L)

6/1/2016: Avg CofC - 1.7, FLEPPC - 56% Medium 12/19/2016: Avg CofC - 1.4, FLEPPC - 47%

Medium 23/32

AGM 2011 (6 µg/L) 2012 (8 µg/L) Medium 2015 (24 µg/L) 2016 (15 µg/L) 2017 (8 µg/L)

AGM 2011 (0.78 mg/L) 2012 (0.62 mg/L) Medium 2015 (0.91 mg/L) 2016 (0.95 mg/L) 2017 (0.87 mg/L) AGM 2011 (0.01 mg/L) 2012 (0.01 mg/L) Medium 2015 (0.03 mg/L) 2016 (0.02 mg/L) 2017 (0.02 mg/L)

LVI (n=2) WBID Mean (24) Medium Mean 1 (29), Mean 2 (20)

AGM 2015 (13 µg/L) Medium 2017 (19 µg/L) 2018 (14 µg/L)

AGM 2015 (0.84 mg/L) Medium 2017 (1.05 mg/L) 2018 (0.97 mg/L)

AGM 2015 (0.02 mg/L) Medium 2017 (0.03 mg/L) 2018 (0.03 mg/L)

AGM 2011 (31 µg/L) Medium 2015 (50 µg/L) 2016 (33 µg/L) 2017 (39 µg/L) AGM 2009 (53 µg/L) 2010 (63 µg/L) 2011 (59 µg/L) Medium 2012 (66 µg/L) 2013 (54 µg/L) 2014 (50 µg/L) 2015 (44 µg/L) AGM 2009 (2.28 mg/L) 2010 (2.02 mg/L) 2011 (2.22 mg/L) Medium 2012 (2.41 mg/L) 2013 (1.98 mg/L) 2014 (1.94 mg/L) 2015 (1.73 mg/L)

AGM 2009 (0.07 mg/L) 2010 (0.07 mg/L) 2011 (0.08 mg/L) Medium 2012 (0.08 mg/L) 2013 (0.08 mg/L) 2014 (0.08 mg/L) 2015 (0.06 mg/L)

LVI (n=6) WBID Mean (37) Medium Mean 1 (42), Mean 2 (35)

AGM 2011 (16 µg/L) 2012 (21 µg/L) 2013 (23 µg/L) Medium 2014 (19 µg/L) 2015 (26 µg/L) 2016 (22 µg/L) 2017 (25 µg/L)

Annual Geometric Mean(s) 2008 (27 µg/L) 2009 (31 µg/L) 2010 (29 µg/L) Medium 2011 (20 µg/L) 2012 (30 µg/L) 2013 (26 µg/L) 2014 (24 µg/L) 2015 (26 µg/L)

Annual Geometric Mean(s) 2008 (1.25 mg/L) 2009 (0.96 mg/L) 2010 (0.90 mg/L) Medium 2011 (1.21 mg/L) 2012 (1.39 mg/L) 2013 (1.32 mg/L) 2014 (1.43 mg/L) 2015 (1.35 mg/L) Annual Geometric Mean(s) 2008 (30 µg/L) 2009 (26 µg/L) Medium 2010 (23 µg/L) 2011 (20 µg/L) 2012 (35 µg/L) 2013 (29 µg/L) 2014 (19 µg/L)

Annual Geometric Mean(s) 2008 (1.32 mg/L) 2009 (1.31 mg/L) Medium 2010 (1.35 mg/L) 2011 (1.29 mg/L) 2012 (1.51 mg/L) 2013 (1.50 mg/L) 2014 (1.27 mg/L) Annual Geometric Mean(s) 2008 (12 µg/L) Medium 2010 (13 µg/L) 2012 (27 µg/L) 2013 (24 µg/L) 2014 (30 µg/L)

Annual Geometric Mean(s) 2008 (1.61 mg/L) Medium 2010 (1.82 mg/L) 2012 (2.00 mg/L) 2013 (1.89 mg/L) 2014 (1.95 mg/L)

Annual Geometric Mean(s) 2008 (36 µg/L) 2009 (36 µg/L) Medium 2010 (38 µg/L) 2011 (44 µg/L) 2012 (35 µg/L) 2013 (28 µg/L) 2014 (23 µg/L)

Annual Geometric Mean(s) 2008 (1.36 mg/L) 2009 (1.48 mg/L) Medium 2010 (1.43 mg/L) 2011 (1.65 mg/L) 2012 (1.36 mg/L) 2013 (1.31 mg/L) 2014 (1.19 mg/L)

Annual Geometric Mean(s) 2008 (0.04 mg/L) 2009 (0.04 mg/L) Medium 2011 (0.06 mg/L) 2012 (0.05 mg/L) 2013 (0.04 mg/L) 2014 (0.02 mg/L) Low 7/19

Low 6/22

Low 11/14

Medium 15/40

AGM 2012 (43 µg/L) Medium 2014 (32 µg/L) 2015 (54 µg/L)

AGM 2012 (2.14 mg/L) Medium 2014 (1.44 mg/L) 2015 (1.42 mg/L)

AGM 2012 (0.20 mg/L) Medium 2014 (0.30 mg/L) 2015 (0.32 mg/L)

LVI (n=3) WBID Mean (38) Medium Mean 1 (48), Mean 2 (47)

AGM Medium 2016 (0.74 mg/L) 2017 (0.68 mg/L)

Low 12/16 Medium 2008

High 10/20

02/20/2013: Avg CofC - 0.67, FLEPPC - 50% Medium 11/25/2013: Avg CofC - 0.55, FLEPPC - 51.85%

LVI 21FLGW 37017 (23JUL2009: 34) 21FLGW 41633 (21MAY2012: 43) Annual Geometric Mean(s) 2008 (161 µg/L) 2009 (47 µg/L) Medium 2010 (47 µg/L) 2011 (86 µg/L) 2012 (80 µg/L) 2013 (60 µg/L) 2014 (44 µg/L)

Annual Geometric Mean(s) 2008 (4.74 mg/L) 2009 (3.26 mg/L) Medium 2010 (2.15 mg/L) 2011 (2.30 mg/L) 2012 (1.98 mg/L) 2013 (2.02 mg/L) 2014 (1.93 mg/L)

Annual Geometric Mean(s) 2008 (0.11 mg/L) 2009 (0.07 mg/L) Medium 2010 (0.06 mg/L) 2011 (0.05 mg/L) 2012 (0.05 mg/L) 2013 (0.04 mg/L) 2014 (0.05 mg/L) Annual Geometric Mean(s) Medium 2010 (77 µg/L) 2011 (67 µg/L) 2012 (76 µg/L)

Annual Geometric Mean(s) Medium 2010 (0.14 mg/L) 2011 (0.14 mg/L) 2012 (0.13 mg/L)

Annual Geometric Mean(s) Medium 2010 (44 µg/L) 2011 (43 µg/L) 2012 (43 µg/L) Annual Geometric Mean(s) Medium 2009 (0.10 mg/L) 2011 (0.08 mg/L) 2012 (0.09 mg/L)

Annual Geometric Mean(s) Medium 2010 (62 µg/L) 2011 (64 µg/L) 2012 (52 µg/L)

Annual Geometric Mean(s) 2009 (0.08 mg/L) Medium 2010 (0.10 mg/L) 2011 (0.09 mg/L) 2012 (0.08 mg/L)

Annual Geometric Mean(s) 2008 (43 µg/L) 2009 (38 µg/L) Medium 2010 (49 µg/L) 2011 (44 µg/L) 2012 (40 µg/L) 2013 (46 µg/L) 2014 (43 µg/L)

Annual Geometric Mean(s) 2008 (1.53 mg/L) 2009 (1.49 mg/L) Medium 2010 (1.69 mg/L) 2011 (1.62 mg/L) 2012 (1.49 mg/L) 2013 (1.47 mg/L) 2014 (1.37 mg/L)

Annual Geometric Mean(s) 2008 (0.10 mg/L) 2009 (0.10 mg/L) Medium 2010 (0.17 mg/L) 2011 (0.11 mg/L) 2012 (0.12 mg/L) 2013 (0.13 mg/L) 2014 (0.11 mg/L) Low 5/8

Low 16/19

LVI 21FLTPA TPMHAML01L (20JUN2013: 31) 21FLTPA TPMHAML01L (24JUN2015: 20) Annual Geometric Mean(s) Medium 2011 (51 µg/L) 2013 (37 µg/L) 2014 (28 µg/L)

Annual Geometric Mean(s) Medium 2011 (2.16 mg/L) 2013 (2.07 mg/L) 2014 (1.73 mg/L)

Annual Geometric Mean(s) Medium 2011 (0.07 mg/L) 2013 (0.07 mg/L) 2014 (0.06 mg/L)

High 24/43

Annual Geometric Mean(s) 2008 (23 µg/L) 2009 (19 µg/L) Medium 2010 (29 µg/L) 2011 (36 µg/L) 2012 (28 µg/L) 2013 (24 µg/L) 2014 (26 µg/L) Annual Geometric Mean(s) 2008 (1.02 mg/L) 2009 (1.10 mg/L) Medium 2010 (1.33 mg/L) 2011 (1.51 mg/L) 2012 (1.19 mg/L) 2013 (1.28 mg/L) 2014 (1.34 mg/L)

Annual Geometric Mean(s) 2008 (1.02 mg/L) 2009 (1.15 mg/L) Medium 2010 (1.22 mg/L) 2011 (1.35 mg/L) 2012 (1.73 mg/L) 2013 (1.76 mg/L)

Annual Geometric Mean(s) 2011 (0.02 mg/L) Medium 2012 (0.02 mg/L) 2014 (0.02 mg/L) 2015 (0.01 mg/L)

AGM 2011 (14 µg/L) Medium 2015 (25 µg/L) 2016 (46 µg/L) 2017 (34 µg/L) Annual Geometric Mean(s) 2009 (19 µg/L) Medium 2011 (20 µg/L) 2013 (32 µg/L) 2014 (27 µg/L)

Annual Geometric Mean(s) 2008 (0.80 mg/L) 2009 (1.23 mg/L) Medium 2010 (1.07 mg/L) 2011 (1.04 mg/L) 2013 (1.74 mg/L) 2014 (1.58 mg/L)

Low 6/18

Annual Geometric Mean(s) Medium 2010 (33 µg/L) 2011 (34 µg/L) Annual Geometric Mean(s) Medium 2009 (0.09 mg/L) 2011 (0.07 mg/L)

Low

High 41/78

Medium 45/78

Medium Impaired

High

High

High 16/17

Medium 18/25

Medium 9/20

2007 (40 µg/L) Medium 2008 (47 µg/L) AGM 2010 (2.04 mg/L) 2013 (2.49 mg/L) Medium 2014 (2.70 mg/L) 2015 (2.35 mg/L) 2016 (1.93 mg/L) 2017 (2.30 mg/L) AGM 2010 (0.69 mg/L) 2013 (0.62 mg/L) Medium 2014 (0.65 mg/L) 2015 (0.57 mg/L) 2016 (0.42 mg/L) 2017 (0.51 mg/L) Annual Geometric Mean(s) 2009 (41 µg/L) 2010 (30 µg/L) Medium 2011 (31 µg/L) 2012 (33 µg/L) 2013 (32 µg/L) 2014 (34 µg/L)

Annual Geometric Mean(s) 2009 (2.00 mg/L) 2010 (1.83 mg/L) Medium 2011 (1.68 mg/L) 2012 (1.67 mg/L) 2013 (1.69 mg/L) 2014 (1.62 mg/L)

AGM 2010 (4.31 mg/L) 2011 (4.41 mg/L) Medium 2012 (4.54 mg/L) 2013 (3.45 mg/L) 2014 (4.00 mg/L) 2015 (3.94 mg/L)

High 13/14

Low 59/78

Low 12/25

Low 5/24

Low 5/5 Annual Geometric Mean(s) 2008 (31 µg/L) 2009 (27 µg/L) Medium 2010 (31 µg/L) 2011 (39 µg/L) 2012 (27 µg/L) 2013 (13 µg/L) 2014 (34 µg/L)

Annual Geometric Mean(s) 2008 (0.93 mg/L) 2009 (0.88 mg/L) Medium 2010 (1.20 mg/L) 2011 (1.43 mg/L) 2012 (1.05 mg/L) 2013 (0.89 mg/L) 2014 (1.56 mg/L)

Medium 17/25

Low 7/22

2005 (18.1 µg/l) Medium 2008 (33.3 µg/l)

Annual Geometric Mean(s) 2008 (14 µg/L) 2009 (23 µg/L) Medium 2010 (24 µg/L) 2011 (28 µg/L) 2012 (28 µg/L) 2013 (35 µg/L) 2014 (27 µg/L)

Annual Geometric Mean(s) 2008 (0.70 mg/L) 2009 (0.97 mg/L) Medium 2010 (0.82 mg/L) 2011 (1.21 mg/L) 2012 (2.39 mg/L) 2013 (1.82 mg/L) 2014 (1.54 mg/L)

Annual Geometric Mean(s) 2008 (0.02 mg/L) 2009 (0.02 mg/L) Medium 2010 (0.02 mg/L) 2011 (0.03 mg/L) 2012 (0.05 mg/L) 2013 (0.05 mg/L) 2014 (0.02 mg/L)

Annual Geometric Mean(s) 2008 (32 µg/L) 2009 (37 µg/L) Medium 2010 (25 µg/L) 2011 (42 µg/L) 2012 (36 µg/L) 2013 (35 µg/L) 2014 (37 µg/L) Annual Geometric Mean(s) 2008 (1.36 mg/L) 2009 (1.69 mg/L) Medium 2010 (1.35 mg/L) 2011 (1.71 mg/L) 2012 (1.48 mg/L) 2013 (1.64 mg/L) 2014 (1.79 mg/L)

Annual Geometric Mean(s) 2008 (0.04 mg/L) 2009 (0.02 mg/L) Medium 2010 (0.03 mg/L) 2011 (0.03 mg/L) 2012 (0.06 mg/L) 2013 (0.05 mg/L) 2014 (0.02 mg/L)

Annual Geometric Mean(s) 2008 (75 µg/L) 2010 (59 µg/L) Medium 2011 (71 µg/L) 2012 (34 µg/L) 2013 (58 µg/L) 2014 (52 µg/L)

Annual Geometric Mean(s) 2008 (2.63 mg/L) 2010 (2.51 mg/L) Medium 2011 (3.16 mg/L) 2012 (2.31 mg/L) 2013 (2.63 mg/L) 2014 (2.28 mg/L)

Annual Geometric Mean(s) 2008 (0.07 mg/L) Medium 2010 (0.06 mg/L) 2011 (0.06 mg/L) 2012 (0.06 mg/L) 2014 (0.05 mg/L)

Quarterly LVI Means 2010 (Q3) : 43 Medium 2012 (Q4) : 37 2013 (Q3) : 32

Medium 6/29

High 25/41

Low 25/28 Medium 48/51

SCI (n=3) Big Mean (40) Medium Mean 1 (37), Mean 2 (33 )

04/17/2014: Avg CofC - .9, FLEPPC - 63% (21FLPDEM) 12/16/2014: Avg CofC - Medium .1, FLEPPC - 94% (21FLPDEM) 02/10/2016: Avg CofC - .9, FLEPPC - 69% (21FLPDEM)

AGM 2010 (0.10 mg/L) 2011 (0.12 mg/L) 2012 (0.13 mg/L) Medium 2013 (0.13 mg/L) 2014 (0.13 mg/L) 2015 (0.13 mg/L) 2016 (0.14 mg/L) 2017 (0.17 mg/L) ENRB5 (AAM) 2010 (6.7 µg/L) 2011 (7.1 µg/L) 2012 (9.4 µg/L) Medium 2013 (9.5 µg/L) 2014 (8.2 µg/L) 2015 (9.5 µg/L) 2016 (10.3 µg/L)

High 13/20

Low 7/22

Medium 2010 (25 µg/L) Low 2008

Low

Low

AGM Medium 2011 (64 µg/L) 2013 (59 µg/L)

AGM Medium 2011 (1.55 mg/L) 2013 (1.63 mg/L)

AGM Medium 2011 (0.17 mg/L) 2013 (0.14 mg/L)

AGM 2009 (61 µg/L) 2010 (52 µg/L) 2011 (55 µg/L) Medium 2012 (66 µg/L) 2013 (59 µg/L) 2014 (42 µg/L) 2015 (37 µg/L)

AGM 2009 (2.55 mg/L) 2010 (2.17 mg/L) 2011 (2.24 mg/L) Medium 2012 (2.57 mg/L) 2013 (2.34 mg/L) 2014 (2.00 mg/L) 2015 (1.59 mg/L)

AGM 2009 (0.08 mg/L) 2010 (0.06 mg/L) 2011 (0.04 mg/L) Medium 2012 (0.06 mg/L) 2013 (0.04 mg/L) 2014 (0.05 mg/L) 2015 (0.02 mg/L) High 7/9

Low 7/11

Low 49/145

Low 49/145

Low 10/25

High 59/231

Medium

Medium 8/8

Annual Geometric Mean(s) Medium 2010 (94 µg/L) 2011 (156 µg/L) 2012 (144 µg/L)

Annual Geometric Mean(s) 2009 (0.26 mg/L) Medium 2010 (0.20 mg/L) 2011 (0.28 mg/L) 2012 (0.27 mg/L) LVI (n=2) Medium WBID Mean (19) Mean 1 (9), Mean 2 (29)

Medium 15/15

AGM 2015 (4.15 mg/L) Medium 2017 (3.46 mg/L) 2018 (3.29 mg/L)

High

Annual Geometric Mean(s) 2008 (0.82 mg/L) 2009 (0.73 mg/L) 2010 (0.75 mg/L) Medium 2011 (0.86 mg/L) 2012 (0.83 mg/L) 2013 (0.89 mg/L) 2014 (0.96 mg/L) 2015 (0.93 mg/L) Annual Geometric Mean(s) 2011 (18 µg/L) Medium 2012 (21 µg/L) 2013 (21 µg/L) 2014 (16 µg/L) Annual Geometric Mean(s) 2008 (1.95 mg/L) 2009 (2.15 mg/L) Medium 2010 (1.49 mg/L) 2011 (1.75 mg/L) 2012 (1.52 mg/L) 2013 (1.26 mg/L) 2014 (0.79 mg/L)

Low SCI (n=4) WBID Mean (32) Medium Mean 1 (34), Mean 2 (28)

High 11/20

AGM 2011 (0.24 mg/L) 2012 (0.18 mg/L) 2013 (0.22 mg/L) Medium 2014 (0.17 mg/L) 2015 (0.15 mg/L) 2016 (0.16 mg/L) 2017 (0.18 mg/L)

High 8/12

11/07/2012: Avg CofC - .7, FLEPPC - 85% Medium 04/18/2019: Avg CofC - .6, FLEPPC - 88%

Low 6/12

High 8/36

Annual Geometric Mean(s) Medium 2012 (49 µg/L) 2013 (47 µg/L) Annual Geometric Mean(s) 2007 (0.83 mg/L) Medium 2011 (0.83 mg/L) 2012 (1.32 mg/L) 2013 (1.18 mg/L)

Annual Geometric Mean(s) 2007 (0.04 mg/L) Medium 2011 (0.06 mg/L) 2012 (0.07 mg/L) 2013 (0.07 mg/L)

LVI (n=2) Medium WBID Mean (13) Mean 1 (7), Mean 2 (18)

High 2004

LVI 21FLTPA Medium 27584418154127 (13AUG2008: 10; 09AUG2012: 8) Annual Geometric Mean(s) 2008 (74 µg/L) 2009 (67 µg/L) Medium 2010 (61 µg/L) 2011 (150 µg/L) 2012 (213 µg/L) 2013 (110 µg/L) 2014 (101 µg/L)

Annual Geometric Mean(s) 2008 (2.26 mg/L) 2009 (2.27 mg/L) Medium 2010 (2.12 mg/L) 2011 (3.97 mg/L) 2012 (5.39 mg/L) 2013 (3.27 mg/L) 2014 (3.29 mg/L) Annual Geometric Mean(s) 2008 (0.21 mg/L) 2009 (0.17 mg/L) Medium 2010 (0.19 mg/L) 2011 (0.37 mg/L) 2012 (0.67 mg/L) 2013 (0.49 mg/L) 2014 (0.35 mg/L)

LVI 21FLTPA 27585018154453 Medium (13AUG2008: 0) 21FLTPA TPSTAHL01L (07/17/2014: 1)

Annual Geometric Mean(s) 2008 (41 µg/L) 2009 (75 µg/L) Medium 2010 (64 µg/L) 2011 (59 µg/L) 2012 (79 µg/L) 2013 (85 µg/L) 2014 (78 µg/L)

Annual Geometric Mean(s) 2008 (1.40 mg/L) 2009 (1.65 mg/L) Medium 2010 (1.62 mg/L) 2011 (1.61 mg/L) 2012 (2.08 mg/L) 2013 (1.90 mg/L) 2014 (1.87 mg/L)

Annual Geometric Mean(s) 2008 (0.20 mg/L) 2009 (0.26 mg/L) Medium 2010 (0.39 mg/L) 2011 (0.33 mg/L) 2012 (0.41 mg/L) 2013 (0.47 mg/L) 2014 (0.41 mg/L)

Annual Geometric Mean(s) Medium 2010 (47 µg/L) 2011 (37 µg/L) 2014 (60 µg/L) Annual Geometric Mean(s) 2008 (1.52 mg/L) Medium 2009 (1.62 mg/L) 2010 (1.71 mg/L) 2011 (1.55 mg/L) 2014 (2.04 mg/L)

Annual Geometric Mean(s) 2008 (0.11 mg/L) 2009 (0.09 mg/L) Medium 2010 (0.09 mg/L) 2011 (0.07 mg/L) 2012 (0.15 mg/L) 2014 (0.11 mg/L)

Annual Geometric Mean(s) 2010 (102 µg/L) Medium 2011 (133 µg/L) 2012 (87 µg/L) 2013 (3 µg/L)

Annual Geometric Mean(s) Medium 2009 (0.09 mg/L) 2011 (0.05 mg/L) 2012 (0.04 mg/L)

Annual Geometric Mean(s) 2008 (64 µg/L) 2009 (72 µg/L) Medium 2010 (60 µg/L) 2011 (82 µg/L) 2012 (79 µg/L) 2013 (127 µg/L) 2014 (102 µg/L)

Annual Geometric Mean(s) 2008 (1.46 mg/L) 2009 (1.56 mg/L) Medium 2010 (1.39 mg/L) 2011 (4.82 mg/L) 2012 (4.29 mg/L) 2013 (2.56 mg/L) 2014 (1.59 mg/L)

Annual Geometric Mean(s) 2008 (0.27 mg/L) 2009 (0.26 mg/L) Medium 2010 (0.31 mg/L) 2011 (0.80 mg/L) 2012 (0.60 mg/L) 2013 (0.48 mg/L) 2014 (0.24 mg/L) Annual Geometric Mean(s) 2008 (75 µg/L) 2009 (86 µg/L) Medium 2010 (89 µg/L) 2011 (103 µg/L) 2012 (92 µg/L) 2013 (78 µg/L) 2014 (86 µg/L)

Annual Geometric Mean(s) 2008 (1.89 mg/L) 2009 (1.81 mg/L) Medium 2010 (2.11 mg/L) 2011 (2.00 mg/L) 2012 (1.86 mg/L) 2013 (1.83 mg/L) 2014 (1.84 mg/L)

Annual Geometric Mean(s) 2008 (0.32 mg/L) 2009 (0.23 mg/L) Medium 2010 (0.29 mg/L) 2011 (0.29 mg/L) 2012 (0.34 mg/L) 2013 (0.32 mg/L) 2014 (0.27 mg/L)

Low 27/30

Low 14/15

High

High

Medium

Medium

Beach Advisories 2011 (0 days) 2012 (14 days) 2013 (0 days) High 2014 (43 days) 2015 (68 days) 2016 (80 days) 2017 (75 days) Beach Advisories 2011 (6 days) 2012 (19 days) 2013 (7 days) High 2014 (0 days) 2015 (32 days) 2016 (28 days) 2017 (29 days) Beach Advisories 2011 (0 days) 2012 (27 days) 2013 (14 days) High 2014 (21 days) 2015 (37 days) 2016 (37 days) 2017 (68 days)

High

2005 (0 days) 2006 (0 days) 2007 (5 days) High 2008 (0 days) 2009 (21 days) 2010 (0 days) 2011 (72 days)

High

Beach Advisories 2011 (28 days) 2012 (63 days) 2013 (57 days) High 2014 (29 days) 2015 (0 days) 2016 (0 days) 2017 (no advisory) Beach Advisories 2011 (0 days) 2012 (28 days) 2013 (43 days) High 2014 (22 days) 2015 (41 days) 2016 (21 days) 2017 (25 days) Beach Advisories 2011 (0 days) 2012 (28 days) 2013 (49 days) High 2014 (13 days) 2015 (0 days) 2016 (0 days) 2017 (no advisory)

Medium High No Data

Low 64/78

Low 16/27

2006 10/24

Medium

Low

SCI (n=4) Big Mean (33) Medium Mean 1 (22), Mean 2 (41)

AGM 2011 (0.20 mg/L) 2012 (0.27 mg/L) Medium 2013 (0.28 mg/L) 2014 (0.24 mg/L) 2015 (0.19 mg/L) 2016 (0.19 mg/L)

Low

05/01/2014: Avg CofC - .6, FLEPPC - 68% 10/09/2014: Avg CofC - 1.0, FLEPPC - 77% Medium (21FLPDEM) 02/17/2016: Avg CofC - .5, FLEPPC - 81% (21FLPDEM) High 8/9

Low 9/11

SCI (n=4) WBID Mean (28) Medium Mean 1 (20), Mean 2 (28)

Low 15/21

02/25/2015: (less than 2 sq. m.) 12/04/2015: Avg CofC - 0.7, FLEPPC - 84% Medium 12/15/2017: Avg CofC - 0.7, FLEPPC - 70% 03/30/2018: Avg CofC - 1.3, FLEPPC - 75%

AGM 2011 (0.13 mg/L) 2012 (0.11 mg/L) 2013 (0.13 mg/L) Medium 2014 (0.12 mg/L) 2015 (0.13 mg/L) 2016 (0.14 mg/L) 2017 (0.15 mg/L) High 5/6

Low 71/78

AGM 2009 (0.11 mg/L) 2010 (0.15 mg/L) 2011 (0.16 mg/L) Medium 2012 (0.15 mg/L) 2013 (0.17 mg/L) 2014 (0.21 mg/L) 2015 (0.16 mg/L)

LVI (n=3) Medium WBID Mean (12) Mean 1 (11), Mean 2 (9)

AGM 2011 (0.15 mg/L) 2012 (0.09 mg/L) 2013 (0.12 mg/L) Medium 2014 (0.12 mg/L) 2015 (0.13 mg/L) 2016 (0.13 mg/L) 2017 (0.16 mg/L)

SCI (n=4) WBID Mean (25) Medium Mean 1 (18), Mean 2 (23)

Medium 13/52 AGM 2011 (0.16 mg/L) 2012 (0.12 mg/L) 2013 (0.14 mg/L) Medium 2014 (0.12 mg/L) 2015 (0.15 mg/L) 2016 (0.15 mg/L) 2017 (0.13 mg/L)

Medium

Low 34/80

LVI (n=3) WBID Mean (12) Medium Mean 1 (14), Mean 2 (14)

AGM 2013 (99 µg/L) Medium 2014 (135 µg/L) 2015 (74 µg/L)

AGM 2013 (0.18 mg/L) Medium 2014 (0.22 mg/L) 2015 (0.13 mg/L)

High 22/22

SCI (n=3) WBID Mean (34) Medium Mean 1 (26), Mean 2 (42) AGM 2012 (1.99 mg/L) 2013 (2.50 mg/L) 2014 (2.31 mg/L) Medium 2015 (1.89 mg/L) 2016 (2.11 mg/L) 2017 (1.78 mg/L) 2018 (1.57 mg/L) AGM 2012 (0.75 mg/L) 2013 (0.80 mg/L) 2014 (0.74 mg/L) Medium 2015 (0.68 mg/L) 2016 (0.60 mg/L) 2017 (0.68 mg/L) 2018 (0.74 mg/L)

Low

Low No Data

High 22/22

Annual Geometric Mean(s) 2008 (7 µg/L) 2009 (6 µg/L) Medium 2010 (7 µg/L) 2011 (6 µg/L) 2012 (6 µg/L) 2014 (9 µg/L)

High 5/15

AGM 2012 (10.7 µg/L) 2013 (36 µg/L) 2014 (33 µg/L) Medium 2015 (32 µg/L) 2016 (29 µg/L) 2017 (12.1 µg/L) 2018 (36 µg/L) AGM 2012 (0.48 mg/L) 2013 (0.49 mg/L) 2014 (0.66 mg/L) Medium 2015 (0.71 mg/L) 2016 (0.77 mg/L) 2017 (0.65 mg/L) 2018 (0.99 mg/L)

High 6/9

Medium 14/20

High 15/26

Low 9/24

Medium 12/77

Medium 22/24

Medium 10/54

Low 18/53

SCI (n=6) WBID Mean (34) Medium Mean 1 (32), Mean 2 (33) High 8/17

06/19/2014: Avg CofC - 0, FLEPPC - 96% 12/09/2014: (less than 2 sq. m.) 03/31/2015: Avg CofC - 0.4, FLEPPC - 64% Medium 10/26/2015: Avg CofC - 0.5, FLEPPC - 87% 04/05/2017: Avg CofC - 1.3, FLEPPC - 67% 10/18/2017: Avg CofC - 1.0, FLEPPC - 76%

AGM 2011 (0.16 mg/L) 2012 (0.16 mg/L) 2013 (0.16 mg/L) Medium 2014 (0.14 mg/L) 2015 (0.14 mg/L) 2016 (0.17 mg/L) 2017 (0.21 mg/L) 2018 (0.24 mg/L)

High 14/21

03/23/2016: Avg CofC - 1.8, FLEPPC - 36% 05/12/2016: Avg CofC - 1.0, FLEPPC - 69% Medium 05/16/2016: Avg CofC - 1.6, FLEPPC - 62% 10/03/2016: Avg CofC - 2.1, FLEPPC - 32%

Medium

Medium 12/37

Medium 22/55 High 72/76

Low 6/19

Medium 2012

Medium 2005 (66.97)

Annual Geometric Mean(s) 2007 (1.25 mg/L) 2008 (1.18 mg/L) Medium 2009 (1.35 mg/L) 2010 (1.58 mg/L) 2011 (1.75 mg/L) 2012 (1.69 mg/L) 2013 (1.70 mg/L)

Annual Geometric Mean(s) 2007 (0.44 mg/L) 2008 (0.38 mg/L) Medium 2009 (0.47 mg/L) 2010 (0.50 mg/L) 2011 (0.47 mg/L) 2012 (0.52 mg/L) 2013 (0.53 mg/L)

Annual Geometric Mean(s) 2008 (1.27 mg/L) 2009 (1.49 mg/L) Medium 2010 (1.49 mg/L) 2011 (1.00 mg/L) 2012 (1.56 mg/L) 2013 (1.36 mg/L)

Low

High 19/21

Annual Geometric Mean(s) Medium 2009 (170 µg/L) 2010 (117 µg/L) Annual Geometric Mean(s) Medium 2009 (5.14 mg/L) 2010 (3.13 mg/L)

Annual Geometric Mean(s) Medium 2009 (0.25 mg/L) 2010 (0.30 mg/L)

Low 5/22

Low 9/47

AGM 2009 (35 µg/L) 2010 (35 µg/L) 2011 (48 µg/L) Medium 2012 (44 µg/L) 2013 (30 µg/L) 2014 (21 µg/L) 2015 (25 µg/L) 2016 (14 µg/L)

AGM 2009 (1.18 mg/L) 2010 (1.50 mg/L) 2011 (1.64 mg/L) Medium 2012 (1.60 mg/L) 2013 (1.46 mg/L) 2014 (1.03 mg/L) 2015 (1.35 mg/L) 2016 (1.00 mg/L) AGM Medium 2013 (21 µg/L) 2014 (28 µg/L) Annual Geometric Mean(s) Medium 2007 (2.65 mg/L) 2008 (2.57 mg/L) 2009 (2.00 mg/L)

High 240/351

Low 15/95 04/25/2013: Avg CofC - 0, FLEPPC - 50% Medium 12/17/2013: Avg CofC - 1.5, FLEPPC - 50%

01/30/2008: 0% Medium 04/10/2013: 94.95% 12/09/2013: 30.3%

04/10/2013: Avg CofC - 0.9, FLEPPC - 51.09% Medium 12/09/2013: Avg CofC - 1.11, FLEPPC - 49.09%

High 2004

High 2004

High 5/22

Annual Geometric Mean(s) 2008 (9.98 mg/L) 2010 (3.29 mg/L) Medium 2011 (3.60 mg/L) 2012 (3.84 mg/L) 2013 (2.52 mg/L) 2014 (1.37 mg/L)

Medium 16/58

Annual Geometric Mean(s) 2009 (575 µg/L) 2010 (139 µg/L) Medium 2011 (424 µg/L) 2012 (537 µg/L) 2013 (501 µg/L) 2014 (85 µg/L)

Annual Geometric Mean(s) 2009 (12.15 mg/L) 2010 (5.43 mg/L) Medium 2011 (8.14 mg/L) 2012 (10.42 mg/L) 2013 (9.92 mg/L) 2014 (4.27 mg/L) Annual Geometric Mean(s) 2009 (0.29 mg/L) 2010 (0.22 mg/L) Medium 2011 (0.23 mg/L) 2012 (0.32 mg/L) 2013 (0.36 mg/L) 2014 (0.15 mg/L)

Annual Geometric Mean(s) 2008 (10 µg/L) 2009 (8 µg/L) Medium 2010 (7 µg/L) 2011 (8 µg/L) 2012 (9 µg/L) 2013 (10 µg/L) 2014 (13 µg/L)

Annual Geometric Mean(s) 2008 (0.58 mg/L) 2009 (0.43 mg/L) Medium 2010 (0.40 mg/L) 2011 (0.60 mg/L) 2012 (0.65 mg/L) 2013 (0.62 mg/L) 2014 (0.75 mg/L)

Annual Geometric Mean(s) 2008 (0.01 mg/L) 2009 (0.02 mg/L) Medium 2010 (0.02 mg/L) 2011 (0.02 mg/L) 2012 (0.02 mg/L) 2013 (0.02 mg/L) 2014 (0.02 mg/L) Annual Geometric Mean(s) Medium 2008 (56 µg/L) 2009 (57 µg/L) 2010 (63 µg/L)

Annual Geometric Mean(s) Medium 2008 (1.73 mg/L) 2009 (1.95 mg/L) 2010 (1.86 mg/L)

Annual Geometric Mean(s) Medium 2008 (0.12 mg/L) 2009 (0.13 mg/L) 2010 (0.12 mg/L) Annual Geometric Mean(s) 2008 (2.13 mg/L) 2009 (2.41 mg/L) Medium 2010 (2.00 mg/L) 2011 (2.17 mg/L) 2012 (1.48 mg/L) 2013 (0.52 mg/L)

Annual Geometric Mean(s) 2008 (0.22 mg/L) 2009 (0.27 mg/L) Medium 2010 (0.15 mg/L) 2011 (0.24 mg/L) 2012 (0.10 mg/L) 2013 (0.01 mg/L)

Annual Geometric Mean(s) 2008 (76 µg/L) Medium 2010 (57 µg/L) 2011 (87 µg/L) 2012 (78 µg/L) 2014 (63 µg/L)

Annual Geometric Mean(s) 2008 (2.04 mg/L) Medium 2010 (1.65 mg/L) 2011 (1.96 mg/L) 2012 (1.79 mg/L) 2014 (1.69 mg/L)

Annual Geometric Mean(s) 2008 (0.25 mg/L) Medium 2010 (0.13 mg/L) 2011 (0.14 mg/L) 2012 (0.16 mg/L) 2014 (0.15 mg/L)

Low 45/49

High 22/29

Low 9/20

High 36/38 Low 11/19

High 35/52

Low 23/31

High 19/28

Medium

Annual Geometric Mean(s) Medium 2007 (0.41 mg/L) 2008 (1.74 mg/L) 2009 (1.74 mg/L)

High 7/8

High 25/25

Medium

Medium

High 59/99

High 5/7 Low

High 9/9

High 7/11

Low 21/24

High 6/9

High 22/24

High 5/9

Medium

High 8/9

Low 10/13 Low 60/75

High 6/8

High

05/13/2014: Avg CofC - 1.5, FLEPPC - 64% (21FLPDEM) Medium 12/09/2014: Avg CofC - 1.6, FLEPPC - 52% (21FLPDEM)

Low

Medium

Medium

Low 6/18

High 6/9

High 8/9 Medium 29/44

2006 (16 µg/L) Medium 2008 (16 µg/L) 2011 (40 µg/L)

High 26/26

LVI 21FLGW 43510 (13MAY2013: 36) 21FLTPA TPLKBUF01F (15AUG2013: 44)

Annual Geometric Mean(s) Medium 2013 (11 µg/L) 2014 (10 µg/L) Annual Geometric Mean(s) 2008 (0.80 mg/L) 2009 (0.92 mg/L) Medium 2010 (1.03 mg/L) 2011 (0.91 mg/L) 2012 (0.99 mg/L) 2013 (1.05 mg/L) 2014 (0.87 mg/L)

Annual Geometric Mean(s) 2008 (0.01 mg/L) 2009 (0.02 mg/L) Medium 2010 (0.04 mg/L) 2011 (0.03 mg/L) 2012 (0.03 mg/L) 2013 (0.02 mg/L) 2014 (0.05 mg/L)

Low 5/11 Medium 18/37

High 19/26

High 16/47

Medium 30/44

Medium Impaired

High 9/11

AGM 2009 (13 µg/L) 2010 (13 µg/L) 2011 (17 µg/L) Medium 2012 (27 µg/L) 2013 (14 µg/L) 2014 (34 µg/L) 2015 (29 µg/L)

AGM 2009 (1.32 mg/L) 2010 (1.34 mg/L) 2011 (1.47 mg/L) Medium 2012 (1.76 mg/L) 2013 (0.95 mg/L) 2014 (1.20 mg/L) 2015 (1.73 mg/L) AGM Medium 2013 (7.16 mg/L) 2014 (6.46 mg/L)

Low 37/49

ENRB5 (AAM) 2010 (6.6 µg/L) 2011 (5.6 µg/L) 2012 (6.1 µg/L) Medium 2013 (5.9 µg/L) 2014 (6.2 µg/L) 2015 (8.4 µg/L) 2016 (9.3 µg/L)

High 7/12

High 21/47

Medium 24/47

Medium Impaired

LVI (n=2) Medium WBID Mean (10) Mean 1 (14), Mean 2 (5)

AGM 2013 (42 µg/L) 2014 (36 µg/L) Medium 2015 (38 µg/L) 2016 (27 µg/L) 2017 (16 µg/L) AGM 2013 (0.07 mg/L) 2014 (0.09 mg/L) Medium 2015 (0.07 mg/L) 2016 (0.09 mg/L) 2017 (0.05 mg/L)

Medium

High 45/50

AGM 2009 (17 µg/L) 2010 (9 µg/L) Medium 2011 (17 µg/L) 2012 (10 µg/L) 2014 (9 µg/L) 2015 (12 µg/L)

AGM 2009 (0.69 mg/L) 2010 (0.59 mg/L) Medium 2011 (0.76 mg/L) 2012 (0.65 mg/L) 2014 (0.54 mg/L) 2015 (0.75 mg/L)

AGM 2009 (0.01 mg/L) 2010 (0.01 mg/L) Medium 2011 (0.02 mg/L) 2012 (0.01 mg/L) 2014 (0.02 mg/L) 2015 (0.02 mg/L)

High 22/24

Medium

Medium High 6/18

AGM 2011 (0.36 mg/L) 2012 (0.31 mg/L) 2013 (0.34 mg/L) Medium 2014 (0.35 mg/L) 2015 (0.33 mg/L) 2016 (0.26 mg/L) 2017 (0.33 mg/L)

Low 16/26

Low 14/22

High 24/24

High 7/10

High 14/21

AGM Medium 2009 (66 µg/L) 2010 (41 µg/L)

AGM Medium 2009 (2.62 mg/L) 2010 (1.91 mg/L) AGM 2012 (0.24 mg/L) Medium 2014 (0.18 mg/L) 2015 (0.22 mg/L)

AGM Medium 2015 (8 µg/L) 2016 (7 µg/L)

AGM Medium 2015 (0.66 mg/L) 2016 (0.59 mg/L)

Low 7/20

High 8/9

Low 12/25

Low 14/19

High 16/95

High 11/61

High 240/349

Low 7/27

Low 14/21 High 9/9

Low 17/22

Low 17/22

Medium 2012

5/27/2014: Avg CofC - 1.7, FLEPPC - 38% 1/27/2015: Avg CofC - Medium 1.4, FLEPPC - 57% 2/8/2016: Avg CofC - 2.3, FLEPPC - 51%

12/17/2014: Avg CofC - 1.3, FLEPPC - 66% 3/30/2015: Avg CofC - Medium 1.0, FLEPPC - 70% 12/28/2015: Avg CofC - 2.2, FLEPPC - 62%

Low 17/85

Low 14/22

Low 14/83

01/30/2008: (less than 2 sq.m.) 01/30/2008: (less than 2 sq.m.) 11/16/2011: (less than 2 sq.m.) 03/21/2013: Avg CofC - Medium 0.33, FLEPPC - 66.67% 11/05/2013: (less than 2 sq.m.) 11/19/2014: Avg CofC - 0, FLEPPC - 100% 04/07/2015: Avg CofC - 0.06, FLEPPC - 100%

Annual Geometric Mean(s) 2008 (0.61 mg/L) 2009 (0.63 mg/L) Medium 2010 (0.48 mg/L) 2011 (0.47 mg/L) 2012 (0.53 mg/L) 2013 (0.53 mg/L) 2014 (0.54 mg/L) Low 5/6

Low 23/29

Low 6/24

High 23/25

High 10/19

High 55/84

Medium 37/79

Medium Impaired

High 25/26

High 7/9

Low 25/35

High 9/11 Low 9/16

Low 20/24

Low 15/33

Medium 7/11

Low N/A

Low 17/30

Low 7/14

Medium 2008

Low 16/21

AGM High 2009 (39 µg/L) 2011 (35 µg/L)

High 2003

Low

High 24/40

Low 7/13 Low 13/19

High 17/21

High 14/24

ENRB8 (AAM) 2012 (7.9 µg/L) 2013 (9.1 µg/L) Medium 2014 (10.7 µg/L) 2015 (12.5 µg/L) 2016 (13.6 µg/L) 2017 (8.4 µg/L)

Medium 15/39

High 14/16

AGM 2012 (3 µg/L) Medium 2017 (14 µg/L) 2018 (16 µg/L)

High 5/16

04/02/2018: 100% Medium 10/24/2018: 99%

Low 7/24 Medium 6/23

LVI (n=3) Big Mean (38) Mean 1 (36) High Mean 2 (35) Mean 3 (43 [Highlands County Data])

AGM 2009 (32 µg/L) 2010 (30 µg/L) 2011 (27 µg/L) High 2012 (20 µg/L) 2013 (26 µg/L) 2014 (32 µg/L) 2015 (32 µg/L)

AGM 2009 (1.57 mg/L) 2010 (1.55 mg/L) 2011 (1.57 mg/L) High 2012 (1.45 mg/L) 2013 (1.41 mg/L) 2014 (1.55 mg/L) 2015 (1.41 mg/L)

AGM 2009 (0.07 mg/L) 2010 (0.07 mg/L) 2011 (0.07 mg/L) High 2012 (0.06 mg/L) 2013 (0.07 mg/L) 2014 (0.08 mg/L) 2015 (0.07 mg/L)

Medium 2007

12/15/2014: Avg CofC - 1.6, FLEPPC - 63% Medium 3/25/2015: Avg CofC - 1.8, FLEPPC - 55%

2004 (ID) 2006 (ID) Medium 2007 (ID) 2009 (68 µg/L) 2/3/2015: Avg CofC - 2.2, FLEPPC - 38% 6/17/2015: Avg CofC - 1.4, FLEPPC - 56% Medium 5/25/2016: Avg CofC - 0.4, FLEPPC - 89% 12/27/2016: Avg CofC - 0.5, FLEPPC - 62%

Medium 2009

Low 11/12

Low 9/20

High 18/20

Low 25/34

Low 21/23

Low 21/24

High 6/7

Medium 2009

Low 30/64

05/14/2013: Avg CofC - 0.97, FLEPPC - 50% Medium 12/04/2013: Avg CofC - 0.65, FLEPPC - 66.67%

Low 128/704

Medium 2009

Medium 2009 Low 51/73

High 18/19

Medium 26/50

Low 6/12

Medium 2009

Medium 2009

Medium 10/19

High 11/17

03/06/2018: Avg CofC - 1.1, FLEPPC - 55% Medium 04/30/2019: Avg CofC - 2.0, FLEPPC - 41%

High 2003

Medium 2008

Medium 9/21

05/16/2013: Avg CofC - 0.75, FLEPPC - 69.23% Medium 12/03/2013: Avg CofC - 0.28, FLEPPC - 88.06%

Medium 38/74

Low 14/20

Medium 2008 Low 10/14

Medium 8/26

High 7/16

Low 14/24

High 2008 (39.0 µg/l)

Low 103/142

Medium 2008

AGM 2009 (6 µg/L) Medium 2010 (8 µg/L) 2011 (9 µg/L)

AGM 2013 (47 µg/L) High 2014 (43 µg/L) 2015 (43 µg/L) 2016 (31 µg/L)

AGM 2013 (2.15 mg/L) High 2014 (2.10 mg/L) 2015 (2.76 mg/L) 2016 (2.47 mg/L)

AGM 2013 (15 µg/L) Medium 2014 (31 µg/L) 2015 (32 µg/L) 2016 (23 µg/L)

AGM 2013 (0.49 mg/L) Medium 2014 (0.89 mg/L) 2015 (1.19 mg/L) 2016 (1.55 mg/L)

AGM 2013 (0.01 mg/L) Medium 2014 (0.01 mg/L) 2015 (0.02 mg/L) 2016 (0.02 mg/L) Medium 7/17

Medium 25/37

Medium 6/8

Low 7/15

Low 32/86

Medium 18/63

07/30/2013: Avg CofC - 2.17, FLEPPC - 41.18% Medium 01/27/2014: Avg CofC - 2.09, FLEPPC - 28.3%

Low 8/25

Medium 11/21

Low 7/20

Low 117/146

Low 10/24

Medium 2009

05/08/2013: Avg CofC - 0.9, FLEPPC - 63.49% Medium 12/03/2013: Avg CofC - 0.35, FLEPPC - 82.35%

Low 6/20

Low ENRC5: AGM 2008 (0.33 mg/L) 2009 (0.31 mg/L) 2010 (0.38 mg/L) Medium 2011 (0.37 mg/L) 2012 (0.37 mg/L) 2013 (0.46 mg/L) 2014 (0.45 mg/L) 2015 (0.35 mg/L)

Low 11/61

Low 38/114

Annual Geometric Mean(s) 2010 (12 µg/L) 2011 (10 µg/L) Medium 2012 (18 µg/L) 2013 (13 µg/L) 2014 (12 µg/L) 2015 (22 µg/L)

High 17/20

Medium 9/15

Medium 17/17

Low 81/150

Low 36/108

Medium 2009

04/15/2010: 0% Medium 10/19/2010: 68.18% 04/18/2011: 100%

Annual Geometric Mean(s) Medium 2008 (0.40 mg/L) 2010 (0.12 mg/L) 2011 (0.17 mg/L)

Low 42/66 Medium 2008

ENRD2: AAM 2007 (5 µg/L) 2008 (8 µg/L) 2009 (9 µg/L) Medium 2010 (10 µg/L) 2011 (7 µg/L) 2012 (11 µg/L) 2013 (4 µg/L) ENRD2: AAM 2007 (0.65 mg/L) 2008 (0.64 mg/L) 2009 (0.58 mg/L) Medium 2010 (0.64 mg/L) 2011 (0.57 mg/L) 2012 (0.59 mg/L) 2013 (0.44 mg/L)

Low Impaired

2001 (11.41 µg/L) 2002 (9.23 µg/L) 2003 (7.45 µg/L) 2004 (6.69 µg/L) Medium 2005 (11.07 µg/L) 2006 (6.11 µg/L) 2007 (4.42 µg/L)

AGM 2007 (0.54 mg/L) 2008 (0.61 mg/L) 2009 (0.52 mg/L) Medium 2010 (0.60 mg/L) 2011 (0.58 mg/L) 2012 (0.56 mg/L) 2013 (0.49 mg/L)

Medium 2008

Low 39/82

Medium 15/19

Medium 18/18

High 2008 (14.9 µg/l)

Low 22/83 Low 13/66

Low

Low Impaired

Medium 2009

Low

Low Impaired

ENRD7: AAM 2008 (1.15 mg/L) 2009 (0.75 mg/L) 2010 (1.07 mg/L) Medium 2011 (1.07 mg/L) 2012 (0.91 mg/L) 2013 (0.98 mg/L) 2014 (1.21 mg/L)

Low Impaired

High 20/37

High 20/37

High 9/23

Medium 7/18

High 9/13

11/16/2011: (less than 2 sq.m.) 07/22/2014: Avg CofC - Medium 1.23, FLEPPC - 52.5% 01/29/2015: Avg CofC - 1.1, FLEPPC - 46.67% 04/25/2013: Avg CofC - 1.5, FLEPPC - 35.71% Medium 12/18/2013: Avg CofC - 1.19, FLEPPC - 53.57%

ENRD1: AAM 2008 (6.4 µg/L) 2009 (6.4 µg/L) 2010 (8.5 µg/L) Medium 2011 (7.2 µg/L) 2012 (4.9 µg/L) 2013 (5.2 µg/L) 2014 (7.2 µg/L) ENRD1: AAM 2008 (0.62 mg/L) 2009 (0.70 mg/L) 2010 (0.70 mg/L) Medium 2011 (0.74 mg/L) 2012 (0.78 mg/L) 2013 (1.13 mg/L) 2014 (0.82 mg/L)

Low 7/20

Low 36/160

03/18/2013: Avg CofC - 1.82, FLEPPC - 45.45% Medium 11/06/2013: Avg CofC - 0.99, FLEPPC - 76%

Low 21/27

Low 48/66

ENRD1 (AAM) 2008 (0.32 mg/L) 2009 (0.27 mg/L) 2010 (0.41 mg/L) Medium 2011 (0.37 mg/L) 2012 (0.39 mg/L) 2013 (0.49 mg/L) 2014 (0.47 mg/L) ENRY3: AGM 2008 (2.9 µg/L) 2009 (3.7 µg/L) 2010 (3.8 µg/L) Medium 2011 (4.2 µg/L) 2012 (3.2 µg/L) 2013 (5.8 µg/L) 2014 (3.7 µg/L)

High 17/25 Low 8/19

Low 9/17

Medium 5/24

Low 47/172

12/10/2013: Avg CofC - 0.45, FLEPPC - 80.95% Medium 04/09/2014: Avg CofC - 1.46, FLEPPC - 38.71%

Low 56/173

Low 88/328

Low 102/351

ENRD8: AAM Medium 2011 (1.17 mg/L) 2013 (1.19 mg/L)

ENRD8: AAM Medium 2011 (0.63 mg/L) 2013 (0.59 mg/L)

High 15/16

2003 (2.7 µg/l) Medium 2008 (15.2 µg/l)

Medium 14/33

2003 (11.5 µg/l) Medium 2008 (39.1 µg/l)

2003 (7.2 µg/l) Medium 2008 (20.5 µg/l) Medium 9/13

Low 19/29

Medium 8/24

Low 9/34

High 5/16

Medium 7/11

Medium 2009

Low 18/112

Low Impaired

Medium 51/116

Medium 30/62

ENRD8: AAM 2008 (1.25 mg/L) 2009 (1.05 mg/L) 2010 (1.11 mg/L) Medium 2011 (1.11 mg/L) 2012 (1.06 mg/L) 2013 (0.99 mg/L) 2014 (1.09 mg/L) 2015 (0.99 mg/L)

Medium 61/114 ENRD8 (AAM) 2008 (1.01 mg/L) 2009 (0.95 mg/L) Medium 2010 (1.20 mg/L) 2011 (1.25 mg/L) 2012 (1.03 mg/L) 2013 (1.09 mg/L) 2003 (7.5 µg/l) 2004 (7.9 µg/l) Medium 2005 (6.4 µg/l) 2006 (11.5 µg/l)

Medium 2009

High Impaired

High Impaired

Medium 2009

Medium 7/8

Medium 2008

2003 (13.12 µg/L) 2006 Medium (14.93 µg/L)

High Impaired

ENRD4 (AAM) 2012 (0.63 mg/L) 2013 (0.78 mg/L) 2014 (0.67 mg/L) Medium 2015 (0.80 mg/L) 2016 (0.93 mg/L) 2017 (0.90 mg/L) 2018 (0.58 mg/L) ENRD4 (AAM) 2012 (0.16 mg/L) 2013 (0.21 mg/L) Medium 2014 (0.17 mg/L) 2015 (0.19 mg/L) 2016 (0.20 mg/L) 2017 (0.26 mg/L) ENRD4: AAM 2007 (3.7 µg/L) Medium 2008 (7.1 µg/L) 2009 (9.0 µg/L) 2010 (4.1 µg/L) ENRD4 (AAM) 2012 (0.54 mg/L) 2013 (0.69 mg/L) Medium 2014 (0.62 mg/L) 2015 (0.72 mg/L) 2016 (0.83 mg/L) 2017 (0.86 mg/L)

Medium 2008

High Impaired

Medium 2008

ENRD5 (AAM) 2012 (0.46 mg/L) 2013 (0.43 mg/L) 2014 (0.40 mg/L) Medium 2015 (0.64 mg/L) 2016 (0.66 mg/L) 2017 (0.66 mg/L) 2018 (0.74 mg/L) 2019 (0.68 mg/L)

Medium 2008

ENRD9: AAM 2007 (0.40 mg/L) 2008 (0.58 mg/L) 2009 (0.59 mg/L) Medium 2010 (0.78 mg/L) 2011 (0.70 mg/L) 2012 (0.90 mg/L) 2013 (0.91 mg/L)

High Impaired

AGM Insufficient Data ENRD5 (AAM) 2012 (4.1 µg/L) 2013 (6.6 µg/L) Medium 2014 (3.1 µg/L) 2015 (7.2 µg/L) 2016 (7.4 µg/L) 2017 (7.5 µg/L) 2018 (7.0 µg/L) 2019 (2.3 µg/L) ENRD5 (AAM) 2012 (0.61 mg/L) 2013 (0.50 mg/L) 2014 (0.46 mg/L) Medium 2015 (0.73 mg/L) 2016 (0.72 mg/L) 2017 (0.75 mg/L) 2018 (0.71 mg/L) 2019 (0.69 mg/L)

High Impaired

ENRD6 (LTA) Medium (3.9 µg/L)

ENRD6 (LTA) Medium (0.62 mg/L)

Low 7/23

Medium 78/123

Low 80/125

Low Impaired

High NA

AGM 2012 (10 µg/L) 2013 (9 µg/L) 2014 (6 µg/L) Medium 2015 (7 µg/L) 2016 (15 µg/L) 2017 (14 µg/L) 2018 (6 µg/L) 2019 (4 µg/L) Medium 2008

ENRD5 (AAM) 2012 (0.55 mg/L) 2013 (0.65 mg/L) 2014 (0.49 mg/L) Medium 2015 (0.64 mg/L) 2016 (0.76 mg/L) 2017 (0.78 mg/L) 2018 (0.77 mg/L) 2019 (0.70 mg/L)

Medium 8/19

AGM Medium 2015 (44 µg/L) 2017 (50 µg/L)

AGM 2015 (2.60 mg/L) Medium 2016 (2.20 mg/L) 2017 (2.53 mg/L) 2018 (2.75 mg/L)

AGM 2015 (0.14 mg/L) Medium 2016 (0.12 mg/L) 2017 (0.13 mg/L) 2018 (0.06 mg/L)

Low 7/18

Low 12/12

Low 18/86

Low 5/17

Low 23/86 Medium 2011

Medium 2008

High 10/30

Low 12/24

Low 37/45

Low 19/47

Low 6/19

ENRBB1: LTAAM 16.92 Medium µg/L

Low 17/27

Low 17/48

Medium 9/22

High 9/10

Medium 5/20

Medium 6/24

Medium 2008 Medium 5/9

Medium 2008

Low 27/30

Medium 7/38

Low 5/8

High 6/17

Medium 8/17

Medium 9/9

Medium 6/6

Medium 6/7

Medium 23/29

ENRBB1: LTAAM = Medium 11.0 µg/L

Medium 10/21

Medium 2008

Low 2008 Medium 10/16

Low 19/19

Low 48/72

Medium 2008

Low 23/28

High 9/9

Low 10/17

High 9/11

Medium 2008

Low 8/33

Low 12/28

Medium 12/17

Medium 2008 High 10/10

Medium 6/21

Medium 12/13

Low 13/29

Medium 12/20

AGM Insufficient Data Medium ENRBB1 (LTAAM) (11.2 µg/L)

Medium 2008

Low 18/30

High 10/10

Medium 21/81

AGM Medium 2017 (30 µg/L) 2018 (18 µg/L)

Low 19/54

Medium 16/20 High 10/10

High 7/11

Low 9/20

High 6/11

High 8/12

High 7/11

High 10/11

Low

Medium 2008

Medium 15/18

Medium 14/18

Medium 19/19 High 6/10

Low 15/34

ENRS1 (AGM) 2010 (6.3 µg/L) Medium 2011 (7.7 µg/L) 2012 (5.2 µg/L) 2013 (1.9 µg/L) ENRS1 (AGM) 2010 (0.64 mg/L) Medium 2011 (1.00 mg/L) 2013 (0.98 mg/L)

Low 3/39

2008 (7 µg/L) Medium 2009 (8 µg/L) 2010 (14 µg/L)

Medium 24/42

Low N/A

Medium 13/13

Low N/A

ENRT1 (AGM) 2010 (0.66 mg/L) 2011 (0.59 mg/L) Medium 2014 (0.62 mg/L) 2015 (0.84 mg/L) 2017 (0.76 mg/L)

Low N/A ENRY10 (AAM) 2010 (12.8 µg/L) 2011 (12.3 µg/L) 2012 (12.7 µg/L) Medium 2013 (9.3 µg/L) 2014 (9.5 µg/L) 2015 (8.7 µg/L) 2016 (7.5 µg/L) 2017 (7.2 µg/L)

High 22/29

Medium 2008

Medium 2008

Medium 12/33

Low 16/21

Medium 8/13

Low n/a

Low Impaired

Medium 2008

Low 13/48

Medium 2008

High 7/16

Medium 2008

Low

Low

Low

Low 6/21

Low

High 21/52 Low 8/23

Low

Low

Low

Low

Low

Low

Low n/a

Medium 7/31

AGM Medium 2016 (12 µg/L) 2017 (23 µg/L)

ENRL6 (PCT) Medium 28/85

Low N/A

Medium 14/14

Medium 6/7

Low 6/19

Medium 8/14

Low 10/14

Low 6/28

Medium 5/5

AGM(s) 2007 (1.19 mg/L) 2008 (2.34 mg/L) Medium 2009 (2.66 mg/L) 2010 (1.83 mg/L) 2011 (1.82 mg/L) Medium 70/98

SCI (n=2) WBID Mean (40) Medium Mean 1 (33), Mean 2 (47)

AGM 2012 (0.36 mg/L) 2013 (0.47 mg/L) 2014 (0.40 mg/L) Medium 2015 (0.40 mg/L) 2016 (0.32 mg/L) 2017 (0.29 mg/L) 2018 (0.30 mg/L) 2019 (0.22 mg/L)

Medium 52/95

Low n/a

Medium 21/32

Medium 21/32

Low 8/24

Low 8/11

Medium 12/27

Medium 7/15 Low 5/9

06/24/2014: Avg CofC - 1.6, FLEPPC - 46% Medium 10/09/2014: Avg CofC - .5, FLEPPC - 81%

AGM 2012 (0.19 mg/L) 2013 (0.32 mg/L) 2014 (0.37 mg/L) Medium 2015 (0.32 mg/L) 2016 (0.24 mg/L) 2017 (0.35 mg/L) 2018 (0.54 mg/L)

Medium 2008

Medium 18/43

Low n/a

Low 7/14

Low 12/20

Medium 41/118

Low 21/27

ENRT4 (AGM) 2014 (6.7 µg/L) Medium 2015 (7.9 µg/L) 2016 (8.3 µg/L) 2017 (9.2 µg/L)

Medium 22/66

ENRT4 (AGM) 2011 (5.1 µg/L) 2012 (1.7 µg/L) Medium 2013 (0.9 µg/L) 2014 (0.7 µg/L) 2015 (4.7 µg/L) 2017 (5.5 µg/L) Medium 9/15

AGM(s) 2007 (1.68 mg/L) 2008 (2.46 mg/L) Medium 2009 (2.48 mg/L) 2010 (2.37 mg/L) 2011 (2.26 mg/L)

Medium 8/34

Medium 9/11

Medium 2008

High 2004

Low 9/19

Medium 2008

Low 6/20

06/16/2016: 26% Medium 04/03/2017: 64%

06/16/2016: Avg CofC - 1.8, FLEPPC - 44% Medium 04/03/2017: Avg CofC - 1.6, FLEPPC - 38%

Low 6/7

Medium 55/101 AGM(s) 2007 (1.70 mg/L) Medium 2008 (1.77 mg/L) 2009 (1.80 mg/L)

AGM(s) 2007 (0.22 mg/L) Medium 2008 (0.16 mg/L) 2009 (0.15 mg/L)

Medium 54/74

09/24/2014: Avg CofC - 2.4, FLEPPC - 44% Medium 12/27/2017: Avg CofC - 1.6, FLEPPC - 45%

AGM 2012 (1.76 mg/L) 2013 (1.79 mg/L) 2014 (1.76 mg/L) Medium 2015 (1.61 mg/L) 2016 (1.67 mg/L) 2017 (1.11 mg/L) 2019 (1.36 mg/L) AGM 2012 (0.14 mg/L) 2013 (0.17 mg/L) 2014 (0.18 mg/L) Medium 2015 (0.16 mg/L) 2016 (0.11 mg/L) 2017 (0.11 mg/L) 2019 (0.11 mg/L)

Medium 28/29

Medium 13/21

Medium 10/11

Low 7/14 Medium 2006 (30 µg/L)

High 5/5

11/03/2015: Avg CofC - 1.2, FLEPPC - 51% 02/10/2016: Avg CofC - Medium 2.1, FLEPPC - 33% 08/18/2016: Avg CofC - 2.2, FLEPPC - 41%

09/26/2016: Avg CofC - 1.4, FLEPPC - 52% Medium 06/21/2017: Avg CofC - 2.3, FLEPPC - 33%

AGM 2010 (0.13 mg/L) Medium 2016 (0.14 mg/L) 2017 (0.13 mg/L)

Low 24/35

Low 2/27

Medium

Medium Medium 7/26

06/10/2015: Avg CofC - 1.1, FLEPPC - 47% Medium 09/21/2015: Avg CofC - 1.3, FLEPPC - 37%

AGM 2010 (0.19 mg/L) Medium 2015 (0.15 mg/L) 2016 (0.15 mg/L) 2017 (0.11 mg/L)

Low

Low

High 15/16

LVI (n=2) WBID Mean (34) Medium Mean 1 (31), Mean 2 (36)

AGM 2015 (49 µg/L) Medium 2016 (68 µg/L) 2017 (84 µg/L)

AGM 2015 (1.12 mg/L) Medium 2016 (1.80 mg/L) 2017 (2.43 mg/L) AGM 2015 (0.16 mg/L) Medium 2016 (0.19 mg/L) 2017 (0.31 mg/L)

SCI (n=2) WBID Mean (15) Medium Mean 1 (11), Mean 2 (19)

AGM 2011 (55 µg/L) 2014 (42 µg/L) Medium 2015 (75 µg/L) 2016 (61 µg/L) 2017 (43 µg/L) AGM 2011 (3.83 mg/L) 2014 (2.33 mg/L) Medium 2015 (2.55 mg/L) 2016 (2.86 mg/L) 2017 (3.33 mg/L) AGM 2011 (0.31 mg/L) 2014 (0.13 mg/L) Medium 2015 (0.12 mg/L) 2016 (0.17 mg/L) 2017 (0.16 mg/L)

AGM 2015 (0.34 mg/L) Medium 2016 (0.29 mg/L) 2017 (0.27 mg/L)

Low 22/52

Low 6/6

Low AGM 2015 (0.14 mg/L) Medium 2016 (0.22 mg/L) 2017 (0.29 mg/L)

Medium 26/26

SCI (n=5) WBID Mean (33) Medium Mean 1 (38), Mean 2 (34)

Medium

Low 7/10

Low Low AGM 2012 (1.11 mg/L) Medium 2013 (1.12 mg/L) 2014 (1.06 mg/L) 2015 (1.18 mg/L)

Medium

AGM 2013 (12 µg/L) Medium 2014 (31 µg/L) 2015 (46 µg/L) 2016 (73 µg/L) AGM 2011 (4.77 mg/L) 2013 (1.96 mg/L) Medium 2014 (2.30 mg/L) 2015 (2.51 mg/L) 2016 (3.21 mg/L) AGM 2011 (0.32 mg/L) 2013 (0.12 mg/L) Medium 2014 (0.14 mg/L) 2015 (0.14 mg/L) 2016 (0.17 mg/L)

11/14/2011: Avg CofC - 3.0, FLEPPC - 25% 04/12/2017: Avg CofC - Medium 2.2, FLEPPC - 35% 08/31/2017: Avg CofC - 2.1, FLEPPC - 30%

AGM 2011 (2.05 mg/L) 2012 (2.72 mg/L) 2013 (2.42 mg/L) Medium 2014 (2.37 mg/L) 2015 (1.51 mg/L) 2016 (1.33 mg/L) 2017 (1.66 mg/L)

Medium 35/38

Medium 22/23

Medium 7/9

Medium 10/49

AGM 2011 (14 µg/L) Medium 2017 (15 µg/L) 2018 (16 µg/L) AGM 2011 (1.49 mg/L) Medium 2017 (1.23 mg/L) 2018 (1.26 mg/L)

AGM 2011 (0.02 mg/L) Medium 2017 (0.02 mg/L) 2018 (0.02 mg/L)

Medium 50/52

AGM 2012 (4.12 mg/L) Medium 2013 (3.50 mg/L) 2015 (1.75 mg/L)

Assessment based on Medium DOH Fish Tissue Studies

07/25/2016: 45% High 11/01/2016: 27%

AGM Medium 2016 (2.90 mg/L) 2017 (2.94 mg/L)

AGM Medium 2016 (1.25 mg/L) 2017 (2.76 mg/L)

Medium vp=9/9

Medium Low vp=19/57

Medium 7/13

02/21/2013: Avg CofC - 2.39, FLEPPC - 32.79% Medium 10/21/2013: Avg CofC - 1.7, FLEPPC - 48.19%

High vp=66/175

Medium vp=8/19

Medium 14/38

Low vp=11/21

08/15/2013: Avg CofC - 1.25, FLEPPC - 52.05% Medium 11/25/2013: Avg CofC - 1.28, FLEPPC - 32.73%

04/02/2013: Avg CofC - 2.01, FLEPPC - 32.5% Medium 08/13/2013: Avg CofC - 1.67, FLEPPC - 47.62%

Annual Geometric Mean(s) 2008 (2.50 mg/L) Medium 2010 (1.75 mg/L) 2011 (2.00 mg/L) 2013 (1.65 mg/L) AGM(s) 2009 (19 µg/L) Medium 2011 (25 µg/L) 2012 (41 µg/L)

AGM 2013 (0.17 mg/L) 2014 (0.18 mg/L) Medium 2015 (0.20 mg/L) 2016 (0.20 mg/L) 2017 (0.21 mg/L) 2018 (0.27 mg/L)

Medium vp=86/146

Medium 25/72 08/15/2013: Avg CofC - 1.67, FLEPPC - 48.1% Medium 11/25/2013: Avg CofC - 0.11, FLEPPC - 93.75%

AGM 2017 (11 µg/L) Medium 2018 (9 µg/L) 2019 (8 µg/L)

AGM 2017 (0.96 mg/L) Medium 2018 (0.88 mg/L) 2019 (0.86 mg/L)

AGM 2017 (0.02 mg/L) Medium 2018 (0.02 mg/L) 2019 (0.02 mg/L)

01/26/2012: 89.9% High 11/01/2012: 89.13%

AGM 2012 (38 µg/L) Medium 2014 (28 µg/L) 2015 (15 µg/L) 2017 (46 µg/L)

AGM 2012 (1.74 mg/L) Medium 2014 (1.61 mg/L) 2015 (1.56 mg/L) 2017 (1.52 mg/L)

AGM 2012 (0.06 mg/L) Medium 2014 (0.08 mg/L) 2015 (0.07 mg/L) 2017 (0.07 mg/L) 02/29/2012: Avg CofC - 3.1, FLEPPC - 26% 12/03/2012: Avg CofC - 2.7, FLEPPC - 29% Medium 02/01/2017: Avg CofC - 1.9, FLEPPC - 44% 11/27/2017: Avg CofC - 1.5, FLEPPC - 41%

ENRAA11 (AGM) 2010 (4.3 µg/L) 2011 (10.5 µg/L) 2012 (12.6 µg/L) Medium 2013 (9.6 µg/L) 2014 (2.4 µg/L) 2015 (15.9 µg/L) 2016 (28.3 µg/L) 2017 (4.5 µg/L)

ENRAA11 (AGM) 2010 (0.99 mg/L) 2011 (1.08 mg/L) 2012 (1.33 mg/L) Medium 2013 (1.03 mg/L) 2014 (0.85 mg/L) 2015 (1.34 mg/L) 2016 (1.49 mg/L) 2017 (1.21 mg/L)

ENRAA11 (AGM) 2010 (0.021 mg/L) 2011 (0.040 mg/L) 2012 (0.035 mg/L) Medium 2013 (0.033 mg/L) 2014 (0.021 mg/L) 2015 (0.045 mg/L) 2016 (0.050 mg/L) 2017 (0.037 mg/L)

Low N/A

ENRAA12 (AGM) 2010 (5.3 µg/L) 2011 (7.5 µg/L) 2012 (9.4 µg/L) Medium 2013 (7.8 µg/L) 2014 (5.7 µg/L) 2015 (7.1 µg/L) 2016 (15.2 µg/L) 2017 (2.4 µg/L)

ENRAA12 (AGM) 2010 (0.57 mg/L) 2011 (0.68 mg/L) 2012 (0.95 mg/L) Medium 2013 (0.71 mg/L) 2014 (0.74 mg/L) 2015 (0.73 mg/L) 2016 (0.95 mg/L) 2017 (0.68 mg/L) High NA

ENRAA13 (AGM) 2010 (4.2 µg/L) 2011 (5.0 µg/L) 2012 (5.2 µg/L) Medium 2013 (4.5 µg/L) 2014 (4.0 µg/L) 2015 (5.7 µg/L) 2016 (8.1 µg/L) 2017 (2.8 µg/L)

Medium 70/71

Medium 9/44

AGM 2010 (10 µg/L) 2011 (18 µg/L) 2012 (32 µg/L) Medium 2013 (10 µg/L) 2015 (10 µg/L) 2016 (10 µg/L) 2017 (26 µg/L)

Medium 59/73

Low N/A

Low Impaired

Low Impaired High NA

Low N/A

Low N/A

Low N/A

Annual Geometric Mean(s) 2008 (0.09 mg/L) Medium 2009 (0.10 mg/L) 2011 (0.10 mg/L) 2013 (0.07 mg/L)

Low 6/20

Chl-a annual means Medium were 33.5 µg/L (2003), and 5.375 µg/L (2005).

Low 14/35

High 9/15

Medium 2008

Low 10/13

AGM(s) 2007 (0.03 mg/L) Medium 2009 (0.04 mg/L) 2010 (0.04 mg/L) 2011 (0.04 mg/L) AGM 2015 (8 µg/L) Medium 2016 (8 µg/L) 2017 (24 µg/L) 2018 (33 µg/L) AGM 2014 (0.67 mg/L) Medium 2015 (0.59 mg/L) 2017 (0.62 mg/L) 2018 (0.66 mg/L)

AGM Medium 2017 (0.80 mg/L) 2018 (0.63 mg/L)

High 13/17

High 11/31

High 8/12

AGM 2017 (24 µg/L) Medium 2018 (27 µg/L) 2019 (27 µg/L)

AGM 2017 (0.04 mg/L) Medium 2018 (0.04 mg/L) 2019 (0.04 mg/L)

AGM 2017 (31 µg/L) Medium 2018 (39 µg/L) 2019 (14 µg/L)

AGM 2017 (1.43 mg/L) Medium 2018 (1.98 mg/L) 2019 (1.08 mg/L) AGM 2017 (0.04 mg/L) Medium 2018 (0.04 mg/L) 2019 (0.04 mg/L)

High 14/17

Low 18/60

03/02/2012: Avg CofC - 1.8, FLEPPC - 63% 11/13/2017: (less than 2 sq. m.) Medium 05/30/2018: Avg CofC - 2.4, FLEPPC - 30% 02/28/2019: Avg CofC - 2.1, FLEPPC - 30%

AGM 2012 (13 µg/L) 2013 (13 µg/L) Medium 2014 (23 µg/L) 2015 (31 µg/L) 2016 (15 µg/L)

AGM 2012 (0.05 mg/L) 2013 (0.04 mg/L) Medium 2014 (0.05 mg/L) 2015 (0.05 mg/L) 2016 (0.03 mg/L)

Low 9/23

Quarterly LVI Means Medium 2013 (Q3) : 6 2013 (Q4) : 8

Low 17/69

AGM 2017 (7 µg/L) Medium 2018 (10 µg/L) 2019 (8 µg/L) AGM 2017 (0.59 mg/L) Medium 2018 (0.59 mg/L) 2019 (0.54 mg/L)

AGM 2017 (0.02 mg/L) Medium 2018 (0.02 mg/L) 2019 (0.02 mg/L)

04/03/2012: (less than 2 sq. m.) 04/29/2014: Avg CofC - .9, FLEPPC - 86% 04/01/2015: Avg CofC - Medium .2, FLEPPC - 92% 08/01/2016: Avg CofC - .6, FLEPPC - 87% 03/01/2017: Avg CofC - 1.8, FLEPPC - 50%

AGM 2012 (15 µg/L) 2015 (16 µg/L) Medium 2016 (31 µg/L) 2017 (28 µg/L) 2018 (34 µg/L)

AGM 2012 (1.00 mg/L) 2015 (1.32 mg/L) Medium 2016 (1.52 mg/L) 2017 (1.39 mg/L) 2018 (1.40 mg/L)

AGM 2012 (32 µg/L) Medium 2016 (15 µg/L) 2018 (29 µg/L) 2019 (39 µg/L)

Low 7/19 LVI (n=2) WBID Mean (17) Medium Mean 1 (15), Mean 2 (19)

AGM 2012 (57 µg/L) 2014 (29 µg/L) Medium 2015 (55 µg/L) 2016 (33 µg/L) 2018 (31 µg/L)

AGM 2012 (1.41 mg/L) 2013 (1.17 mg/L) Medium 2014 (1.02 mg/L) 2015 (1.17 mg/L) 2016 (1.09 mg/L) 2018 (1.04 mg/L)

AGM 2012 (0.08 mg/L) 2013 (0.07 mg/L) Medium 2014 (0.07 mg/L) 2015 (0.07 mg/L) 2016 (0.05 mg/L) 2018 (0.06 mg/L)

AGM 2012 (0.04 mg/L) Medium 2014 (0.06 mg/L) 2015 (0.07 mg/L) 2016 (0.05 mg/L)

LVI (n=2) Medium WBID Mean (0) Mean 1 (0), Mean 2 (0)

AGM 2012 (67 µg/L) Medium 2014 (60 µg/L) 2015 (68 µg/L) 2016 (26 µg/L) AGM 2012 (1.77 mg/L) 2013 (2.37 mg/L) Medium 2014 (1.42 mg/L) 2015 (1.94 mg/L) 2016 (0.97 mg/L)

AGM 2012 (0.15 mg/L) 2013 (0.18 mg/L) Medium 2014 (0.17 mg/L) 2015 (0.16 mg/L) 2016 (0.09 mg/L)

Low 14/55

AGM(s) 2007 (25 µg/L) 2008 (30 µg/L) Medium 2009 (23 µg/L) 2010 (23 µg/L) 2011 (22 µg/L)

2003 (14.2 µg/l) Medium 2008 (26.8 µg/l)

Low 18/26

Low 7/24

Medium 8/26

Medium 2008

Medium 2008

Low 7/12

AGM 2012 (21 µg/L) 2013 (35 µg/L) Medium 2014 (28 µg/L) 2015 (23 µg/L) 2016 (21 µg/L) AGM 2012 (0.06 mg/L) 2013 (0.08 mg/L) Medium 2014 (0.08 mg/L) 2015 (0.05 mg/L) 2016 (0.05 mg/L)

High 6/29

Low 6/24

High NA

01/30/2017: Avg CofC - 1.5, FLEPPC - 52% Medium 06/13/2017: Avg CofC - 1.9, FLEPPC - 38%

AGM Medium 2012 (0.17 mg/L) 2013 (0.16 mg/L)

High NA

High NA

Medium

06/23/2010: (less than 2 sq. m.) 08/10/2016: Avg CofC - Medium 1.7, FLEPPC - 64% 11/28/2016: Avg CofC - 1.0, FLEPPC - 85%

Medium 6/20 10/24/2016: Avg CofC - .9, FLEPPC - 62% Medium 04/10/2017: Avg CofC - 1.5, FLEPPC - 50%

Low vp=10/30

Medium 26/178

Low 8/20

11/18/2013: Avg CofC - 0.97, FLEPPC - 60% Medium 02/27/2014: Avg CofC - 0.83, FLEPPC - 48.78%

Medium vp=29/47

08/20/2013: Avg CofC - 1.6, FLEPPC - 50% Medium 12/12/2013: Avg CofC - 1.35, FLEPPC - 42.11%

Annual Geometric Mean(s) 2008 (2.02 mg/L) 2009 (2.01 mg/L) Medium 2010 (1.74 mg/L) 2011 (1.74 mg/L) 2012 (1.69 mg/L) 2013 (1.50 mg/L) 2014 (1.42 mg/L)

Low 5/12

High 19/73

08/20/2013: Avg CofC - 1.13, FLEPPC - 62.22% Medium 12/12/2013: Avg CofC - 0.23, FLEPPC - 88.57%

Medium vp=10/28

Medium 19/42 Annual Geometric Mean(s) 2008 (67 µg/L) 2009 (55 µg/L) Medium 2010 (41 µg/L) 2011 (16 µg/L) 2012 (23 µg/L) 2013 (6 µg/L) 2014 (11 µg/L)

Annual Geometric Mean(s) 2008 (3.18 mg/L) 2009 (2.67 mg/L) Medium 2010 (2.34 mg/L) 2011 (1.86 mg/L) 2012 (2.32 mg/L) 2013 (1.71 mg/L) 2014 (1.58 mg/L)

Annual Geometric Mean(s) 2008 (0.14 mg/L) 2009 (0.14 mg/L) Medium 2010 (0.13 mg/L) 2011 (0.06 mg/L) 2012 (0.14 mg/L) 2013 (0.06 mg/L) 2014 (0.05 mg/L)

Low

Medium 9/48

Low 9/29

High vp=7/22

Low

Medium 12/27

09/19/2013: Avg CofC - 1.3, FLEPPC - 59% Medium 12/30/2013: Avg CofC - 1.8, FLEPPC - 46%

AGM 2010 (0.14 mg/L) Medium 2011 (0.10 mg/L) 2012 (0.16 mg/L) Medium 2008

07/24/2013: Avg CofC - 2.8, FLEPPC - 34% 11/26/2013: Avg CofC - Medium .2, FLEPPC - 85% 02/09/2017: Avg CofC - 1.8, FLEPPC - 53%

High 18/22

Low 13/61

AGM 2009 (19 µg/L) Medium 2010 (29 µg/L) 2011 (27 µg/L) 2014 (21 µg/L) AGM 2009 (28 µg/L) Medium 2010 (38 µg/L) 2011 (21 µg/L) 2014 (16 µg/L)

AGM 2009 (1.13 mg/L) Medium 2010 (1.33 mg/L) 2014 (0.88 mg/L)

AGM 2009 (27 µg/L) Medium 2010 (21 µg/L) 2011 (25 µg/L) 2014 (13 µg/L)

AGM 2009 (1.57 mg/L) 2010 (1.54 mg/L) Medium 2011 (1.67 mg/L) 2013 (1.18 mg/L) 2014 (0.91 mg/L) AGM 2009 (0.06 mg/L) 2010 (0.06 mg/L) Medium 2011 (0.05 mg/L) 2013 (0.04 mg/L) 2014 (0.03 mg/L)

AGM 2009 (34 µg/L) Medium 2012 (29 µg/L) 2013 (22 µg/L) 2014 (48 µg/L)

AGM 2009 (1.21 mg/L) 2010 (1.25 mg/L) Medium 2012 (1.35 mg/L) 2013 (1.20 mg/L) 2014 (1.11 mg/L)

AGM 2009 (0.10 mg/L) 2010 (0.10 mg/L) Medium 2012 (0.11 mg/L) 2013 (0.08 mg/L) 2014 (0.10 mg/L)

AGM 2009 (1.29 mg/L) 2010 (1.21 mg/L) Medium 2011 (1.12 mg/L) 2012 (1.29 mg/L) 2013 (1.23 mg/L)

AGM 2009 (0.11 mg/L) 2010 (0.12 mg/L) Medium 2011 (0.11 mg/L) 2012 (0.12 mg/L) 2013 (0.10 mg/L)

AGM 2009 (1.56 mg/L) Medium 2011 (1.30 mg/L) 2013 (1.17 mg/L) 2014 (1.04 mg/L) AGM 2009 (38 µg/L) 2010 (43 µg/L) Medium 2011 (34 µg/L) 2013 (32 µg/L) 2014 (31 µg/L)

AGM 2009 (1.54 mg/L) Medium 2010 (1.25 mg/L) 2014 (1.04 mg/L)

AGM 2009 (0.06 mg/L) Medium 2010 (0.06 mg/L) 2014 (0.06 mg/L)

Medium 5/6

AGM Medium 2009 (25 µg/L) 2010 (26 µg/L)

AGM 2009 (0.05 mg/L) Medium 2012 (0.07 mg/L) 2013 (0.10 mg/L) 2014 (0.10 mg/L)

Low 7/17

Medium 5/12

AGM 2009 (71 µg/L) Medium 2014 (74 µg/L) 2015 (39 µg/L)

AGM 2009 (2.55 mg/L) Medium 2014 (1.87 mg/L) 2015 (1.17 mg/L) AGM 2009 (0.11 mg/L) Medium 2014 (0.21 mg/L) 2015 (0.11 mg/L)

AGM Medium 2010 (21 µg/L) 2012 (24 µg/L)

AGM 2009 (0.05 mg/L) 2010 (0.06 mg/L) Medium 2011 (0.05 mg/L) 2012 (0.08 mg/L) 2013 (0.08 mg/L) 2014 (0.05 mg/L)

AGM 2009 (17 µg/L) 2010 (23 µg/L) Medium 2011 (23 µg/L) 2012 (25 µg/L) 2013 (14 µg/L) 2014 (17 µg/L)

AGM 2009 (1.05 mg/L) 2010 (1.05 mg/L) Medium 2011 (1.09 mg/L) 2012 (1.31 mg/L) 2013 (0.98 mg/L) 2014 (0.89 mg/L)

AGM 2009 (0.05 mg/L) 2010 (0.05 mg/L) Medium 2011 (0.06 mg/L) 2012 (0.07 mg/L) 2013 (0.05 mg/L) 2014 (0.05 mg/L)

AGM 2009 (0.06 mg/L) 2010 (0.08 mg/L) Medium 2011 (0.08 mg/L) 2012 (0.12 mg/L) 2013 (0.13 mg/L) 2014 (0.15 mg/L) AGM 2009 (0.10 mg/L) 2010 (0.11 mg/L) Medium 2011 (0.11 mg/L) 2012 (0.08 mg/L) 2013 (0.08 mg/L) 2014 (0.09 mg/L)

AGM 2009 (39 µg/L) 2010 (17 µg/L) Medium 2011 (57 µg/L) 2012 (23 µg/L) 2013 (39 µg/L)

AGM 2009 (1.70 mg/L) 2010 (1.05 mg/L) Medium 2011 (2.01 mg/L) 2012 (1.61 mg/L) 2013 (1.45 mg/L) 2014 (1.14 mg/L)

AGM 2009 (0.09 mg/L) 2010 (0.06 mg/L) Medium 2011 (0.11 mg/L) 2012 (0.10 mg/L) 2013 (0.12 mg/L) 2014 (0.08 mg/L)

AGM 2009 (0.04 mg/L) 2010 (0.04 mg/L) Medium 2011 (0.04 mg/L) 2013 (0.04 mg/L) 2014 (0.03 mg/L)

AGM 2009 (23 µg/L) Medium 2010 (34 µg/L) 2011 (55 µg/L) 2012 (35 µg/L) AGM 2009 (25 µg/L) 2010 (16 µg/L) Medium 2011 (7 µg/L) 2014 (17 µg/L) 2015 (22 µg/L)

AGM 2009 (1.08 mg/L) 2011 (0.87 mg/L) Medium 2012 (0.72 mg/L) 2013 (0.77 mg/L) 2014 (0.71 mg/L) 2015 (0.91 mg/L) AGM 2010 (0.02 mg/L) 2011 (0.02 mg/L) Medium 2012 (0.02 mg/L) 2014 (0.02 mg/L) 2015 (0.02 mg/L)

AGM 2009 (0.04 mg/L) 2010 (0.03 mg/L) Medium 2011 (0.03 mg/L) 2012 (0.04 mg/L) 2013 (0.04 mg/L) 2014 (0.04 mg/L)

AGM 2009 (0.06 mg/L) 2010 (0.08 mg/L) Medium 2011 (0.06 mg/L) 2012 (0.08 mg/L) 2013 (0.08 mg/L) 2014 (0.06 mg/L)

1/31/2013: Avg CofC - 0.9, FLEPPC - 55% Medium 6/26/2013: Avg CofC - 0.9, FLEPPC - 72%

Medium 10/27

AGM 2009 (23 µg/L) 2010 (20 µg/L) Medium 2011 (22 µg/L) 2012 (20 µg/L) 2013 (22 µg/L) 2014 (29 µg/L)

AGM 2009 (1.12 mg/L) 2010 (1.09 mg/L) Medium 2011 (1.15 mg/L) 2012 (1.38 mg/L) 2013 (1.28 mg/L) 2014 (1.17 mg/L)

AGM 2009 (0.06 mg/L) 2010 (0.07 mg/L) Medium 2011 (0.07 mg/L) 2012 (0.09 mg/L) 2013 (0.09 mg/L) 2014 (0.10 mg/L) AGM 2009 (45 µg/L) Medium 2010 (62 µg/L) 2011 (44 µg/L) 2014 (47 µg/L)

AGM 2009 (2.93 mg/L) 2010 (2.48 mg/L) Medium 2011 (2.47 mg/L) 2012 (2.22 mg/L) 2013 (2.45 mg/L) 2014 (1.99 mg/L)

AGM 2009 (0.12 mg/L) 2010 (0.10 mg/L) Medium 2011 (0.11 mg/L) 2012 (0.11 mg/L) 2013 (0.10 mg/L) 2014 (0.10 mg/L)

AGM 2009 (48 µg/L) 2010 (20 µg/L) Medium 2011 (33 µg/L) 2012 (35 µg/L) 2013 (20 µg/L)

AGM 2009 (1.41 mg/L) 2010 (1.35 mg/L) Medium 2011 (1.56 mg/L) 2012 (1.47 mg/L) 2013 (1.58 mg/L)

AGM 2009 (0.08 mg/L) 2010 (0.08 mg/L) Medium 2011 (0.10 mg/L) 2012 (0.11 mg/L) 2013 (0.10 mg/L)

AGM 2010 (32 µg/L) Medium 2011 (24 µg/L) 2012 (34 µg/L) 2014 (44 µg/L) AGM 2009 (1.91 mg/L) 2010 (1.90 mg/L) Medium 2011 (1.68 mg/L) 2012 (2.41 mg/L) 2013 (2.57 mg/L) 2014 (2.02 mg/L)

AGM 2009 (0.06 mg/L) 2010 (0.07 mg/L) Medium 2011 (0.05 mg/L) 2012 (0.10 mg/L) 2013 (0.09 mg/L) 2014 (0.07 mg/L)

AGM 2009 (0.11 mg/L) 2010 (0.08 mg/L) Medium 2011 (0.05 mg/L) 2012 (0.05 mg/L) 2013 (0.07 mg/L) 2014 (0.05 mg/L)

AGM 2009 (1.25 mg/L) 2010 (1.31 mg/L) Medium 2011 (1.18 mg/L) 2012 (1.05 mg/L) 2013 (1.12 mg/L) 2014 (0.70 mg/L)

AGM 2009 (0.11 mg/L) 2010 (0.09 mg/L) Medium 2011 (0.09 mg/L) 2012 (0.10 mg/L) 2013 (0.11 mg/L) 2014 (0.08 mg/L)

AGM 2009 (0.94 mg/L) Medium 2010 (0.96 mg/L) 2014 (0.74 mg/L)

Low 14/54

Medium 10/21

Medium 2011 AGM 2009 (0.78 mg/L) 2010 (0.68 mg/L) Medium 2011 (0.64 mg/L) 2013 (0.73 mg/L) 2014 (0.31 mg/L)

Medium 11/21

Medium 13/19

Medium 2011

3/16/2016: Avg CofC - 1.6, FLEPPC - 64% Medium 6/21/2016: Avg CofC - 0.7, FLEPPC - 83%

4/29/2014: Avg CofC - 0.5, FLEPPC - 60% 12/16/2014: Avg CofC - 1.4, FLEPPC - 41% Medium 8/18/2015: Avg CofC - 1.5, FLEPPC - 56% 12/14/2015: Avg CofC - 1.0, FLEPPC - 45%

AGM 2009 (0.13 mg/L) Medium 2010 (0.14 mg/L) 2014 (0.27 mg/L) 2015 (0.13 mg/L)

4/10/2014: (less than 2 sq.m.) 10/30/2014: Avg CofC - 2.0, FLEPPC - 53% Medium 8/20/2015: Avg CofC - 1.8, FLEPPC - 59% 12/15/2015: Avg CofC - 2.3, FLEPPC - 42%

Low 9/25

2003 (16µg/L) 2004 (21 µg/L) 2005 (17 µg/L) Medium 2006 (16 µg/L) 2007 (20 µg/L) 2008 (21 µg/L) 2009 (25 µg/L)

Medium 23/37

2004 (35 µg/L) Medium 2009 (58 µg/L) 2010 (ID) 3/15/2016: Avg CofC - 2.0, FLEPPC - 55% Medium 6/20/2016: Avg CofC - 2.2, FLEPPC - 45%

AGM Medium 2009 (0.15 mg/L) 2010 (0.21 mg/L)

Medium 12/23

Low 7/24

Medium 2008

High 2005

Medium 18/25

Low 6/25

Medium 10/17

AGM 2009 (0.23 mg/L) 2010 (0.36 mg/L) Medium 2013 (0.15 mg/L) 2014 (0.29 mg/L) 2016 (0.12 mg/L)

High 49/326

2001 (0 days) 2002 (6 days) 2003 (0 days) High 2004 (91 days) 2005 (223 days) 2006 (0 days) 2007 (0 days)

Medium 2008

High 10/30

Medium 2008 Medium 21/70

High 9/23

2003 (21 µg/L) Medium 2004 (26 µg/L) 2009 (33 µg/L)

3/4/2013: Avg CofC - 3.0, FLEPPC - 25% 5/22/2014: Avg CofC - Medium 0.0, FLEPPC - 100% 11/6/2014: Avg CofC - 0.1, FLEPPC - 97%

Medium

Low

Low

Low 8/21

AGM 2012 (2.27 mg/L) 2013 (2.47 mg/L) Medium 2014 (2.69 mg/L) 2015 (2.04 mg/L) 2017 (2.52 mg/L) AGM 2012 (1.00 mg/L) 2013 (0.63 mg/L) Medium 2014 (0.34 mg/L) 2015 (0.60 mg/L) 2017 (0.85 mg/L) 5/5/2014: Avg CofC - 1.3, FLEPPC - 50% Medium 12/1/2014: Avg CofC - 2.3, FLEPPC - 38% AGM 2014 (2.15 mg/L) Medium 2015 (2.63 mg/L) 2016 (1.85 mg/L) 7/8/2014: Avg CofC - 1.8, FLEPPC - 44% 1/14/2015: Avg CofC - Medium 1.5, FLEPPC - 36% 10/27/2015: Avg CofC - 0.9, FLEPPC - 53%

AGM 2010 (0.31 mg/L) 2011 (0.27 mg/L) 2012 (0.27 mg/L) Medium 2013 (0.26 mg/L) 2014 (0.26 mg/L) 2015 (0.33 mg/L) 2016 (0.35 mg/L)

Low

Medium

Low 14/20

Medium

Medium

Low 2010

3/4/2013: Avg CofC - 0.4, FLEPPC - 70% 4/24/2014: (less than 2 sq.m.) Medium 10/29/2014: Avg CofC - 1.0, FLEPPC - 57% 1/13/2016: Avg CofC - 0.1, FLEPPC - 100%

AGM 2009 (2.39 mg/L) 2012 (1.95 mg/L) Medium 2013 (2.57 mg/L) 2014 (2.00 mg/L) 2015 (1.77 mg/L) AGM 2009 (0.20 mg/L) 2010 (0.18 mg/L) 2011 (0.24 mg/L) Medium 2012 (0.27 mg/L) 2013 (0.36 mg/L) 2014 (0.29 mg/L) 2015 (0.27 mg/L)

Medium 24/125

Low 5/17

Medium 9/53

AGM 2015 (25 µg/L) Medium 2016 (19 µg/L) 2017 (18 µg/L) 2018 (47 µg/L) AGM 2011 (1.93 mg/L) 2012 (1.88 mg/L) 2013 (1.57 mg/L) Medium 2014 (1.74 mg/L) 2015 (1.78 mg/L) 2016 (1.89 mg/L) 2017 (2.11 mg/L) 2018 (1.92 mg/L)

AGM 2011 (0.19 mg/L) 2012 (0.18 mg/L) 2013 (0.13 mg/L) Medium 2014 (0.18 mg/L) 2015 (0.15 mg/L) 2016 (0.20 mg/L) 2017 (0.26 mg/L) 2018 (0.22 mg/L)

Medium

Medium 13/31 Low

Medium 18/21

High 2005

2/26/2013: Avg CofC - 0.8, FLEPPC - 59% 4/24/2014: Avg CofC - Medium 2.2, FLEPPC - 36% 10/29/2014: Avg CofC - 1.1, FLEPPC - 69%

AGM Medium 2009 (0.17 mg/L) 2010 (0.15 mg/L)

Medium 2007

Medium 16/49

ENRAA2 (PCT µg/L) Medium 9/20

ENRAA2 (PCT) Medium 12/26

Medium 7/7

AGM Insufficient Data Medium ENRZ6 (AGM) 2017 (13.1 µg/L) 2018 (10.1 µg/L)

Medium 2008

Medium 2008 High 15/83

High 11/52

High 12/16

Medium 2008

High 8/15

Low

Low

Low

Low

Medium 20/52

Low

Low

Medium 8/32 Low

Low 8/30

Medium 9/30

Low

Low

Medium 8/30

Medium 5/14

Medium

2/26/2013: Avg CofC - 1.0, FLEPPC - 43% 4/23/2014: Avg CofC - Medium 1.2, FLEPPC - 44% 9/25/2014: Avg CofC - 0.8, FLEPPC - 57% ENRAA1 (AGM) 2012 (2.1 µg/L) 2013 (1.9 µg/L) Medium 2014 (2.8 µg/L) 2015 (3.6 µg/L) 2016 (2.0 µg/L) 2017 (1.6 µg/L)

Medium 13/35 ENRR1: AGM 2008 (2.1 µg/L) 2009 (1.6 µg/L) 2010 (2.0 µg/L) Medium 2011 (1.7 µg/L) 2012 (2.8 µg/L) 2013 (3.1 µg/L) 2014 (3.2 µg/L) 2015 (1.9 µg/L) 2002 (0 days) 2003 (2 days) 2004 (105 days) High 2005 (35 days) 2006 (6 days) 2007 (1 days) 2008 (0 days)

Medium 6/22

ENRR2 (PCT) Medium 68/412

ENRR2: AGM 2008 (0.023 mg/L) 2009 (0.035 mg/L) 2010 (0.033 mg/L) Medium 2011 (0.026 mg/L) 2012 (0.028 mg/L) 2013 (0.032 mg/L) 2014 (0.056 mg/L) 2015 (0.052 mg/L)

Medium 2010

Medium No Data

Medium 0/2

Medium 23/34

Medium 24/34

Medium 23/47 AGM (11 µg/L) 2010 (3 µg/l) 2011 (2 µg/l) 2012 (1 µg/l) 2013 (2 µg/l) 2014 (3 µg/l) 2015 (3 µg/l) ENRH5 (AGM) 2009 (1.3 µg/L) 2010 (2.6 µg/L) 2011 (2.3 µg/L) Medium 2012 (2.2 µg/L) 2013 (2.1 µg/L) 2014 (2.3 µg/L) 2015 (2.2 µg/L) ENRH9 (AGM) 2009 (0.3 µg/L) 2010 (1.1 µg/L) 2011 (0.9 µg/L) 2012 (0.8 µg/L) 2013 (1.5 µg/L) 2014 (2.0 µg/L) 2015 (2.1 µg/L)

AGM (11 µg/L) 2016 (1 µg/l) ENRH5 (AGM) 2009 (1.7 µg/L) 2010 (3.8 µg/L) Medium 2011 (3.4 µg/L) 2012 (2.2 µg/L) 2013 (3.3 µg/L) 2014 (4.4 µg/L) 2015 (4.0 µg/L)

ENRH5 (AGM) 2009 (0.32 mg/L) 2010 (0.54 mg/L) 2011 (0.27 mg/L) Medium 2012 (0.38 mg/L) 2013 (0.35 mg/L) 2014 (0.30 mg/L) 2015 (0.35 mg/L) ENRH9 (AGM) 2009 (0.4 µg/L) 2010 (0.7 µg/L) 2011 (0.6 µg/L) Medium 2012 (0.8 µg/L) 2013 (1.0 µg/L) 2014 (1.2 µg/L) 2015 (1.7 µg/L)

Low 47/95

Medium 2011

Medium 15/22

2003 (5.32 µg/L) High 2007 (23.09 µg/L) Medium 20/44

Low 19/93

Low 7/31

Low 9/42

Low 17/30

Medium 5/23

Low 10/25

Low 33/152

Low 11/16

Medium 56/106

08/29/2012: (less than 2 sq.m.) 11/08/2012: Avg CofC - 0.62, FLEPPC - 60.34% Medium 03/26/2013: Avg CofC - 1.03, FLEPPC - 51.72% 11/26/2013: Avg CofC - 0.65, FLEPPC - 62.75%

AGM 2011 (0.22 mg/L) Medium 2012 (0.17 mg/L) 2013 (0.19 mg/L) 2014 (0.18 mg/L)

04/17/2012: 95.45% Medium 10/11/2012: 100%

Low 14/78

Low 9/41

Low 17/76

Medium 2009 04/24/2012: Avg CofC - 1.11, FLEPPC - 65.38% 03/26/2013: Avg CofC - Medium 1.27, FLEPPC - 58.23% 11/26/2013: Avg CofC - 0.43, FLEPPC - 79.31%

Medium 59/116

Medium 59/116

High 28/44

High 28/44

03/21/2013: Avg CofC - 0.86, FLEPPC - 44.44% Medium 07/18/2013: Avg CofC - 0.54, FLEPPC - 57.14%

Medium 67/255

03/21/2013: Avg CofC - 0.06, FLEPPC - 97.14% Medium 09/26/2013: Avg CofC - 1.15, FLEPPC - 46.99%

AGM 2008 (1.85 mg/L) 2009 (1.97 mg/L) 2010 (1.57 mg/L) Medium 2011 (1.85 mg/L) 2012 (1.63 mg/L) 2013 (1.56 mg/L) 2014 (1.57 mg/L) 2015 (1.52 mg/L)

High

High High

Medium 140/870

Medium 2009

Medium 151/403

Low 87/187

Medium 2009

Medium 156/439

Low 39/69

Medium 2009

Medium 2009

Medium 2009

Medium 2009

Medium 2009

Medium 100/126

Medium 2009

Medium 2009

Medium 2009

Medium 2009

Low 11/25

Low 24/26

Low 5/25

Medium 2010

High High

Low 10/13

Low 9/53

High 5/21

Low 14/49

AGM 2008 (31 µg/L) 2009 (29 µg/L) 2010 (29 µg/L) Medium 2011 (21 µg/L) 2012 (16 µg/L) 2013 (24 µg/L) 2014 (27 µg/L)

2011 107/271

2002 (20.68 µg/L) 2011 2004 (15.7 µg/L) 2008 (31.06 µg/L)

03/21/2013: Avg CofC - 0.67, FLEPPC - 83.33% Medium 07/18/2013: Avg CofC - 0, FLEPPC - 100%

AGM 2008 (1.78 mg/L) 2009 (1.96 mg/L) 2010 (1.68 mg/L) Medium 2011 (1.69 mg/L) 2012 (1.64 mg/L) 2013 (1.63 mg/L) 2014 (1.59 mg/L) 2015 (1.39 mg/L)

High 2005 2006 (43 µg/L)

High

High

High

Low

Low

High

High

LVI 21FLGW 37860 (04JUN2009: 33) 21FLGW 40243 (23AUG2011: 40) Medium 21FLWPB 28010470 (02DEC2013: 43) 21FLWPB 28010737 (07AUG2008: 45) 21FLWPB 41842 (14NOV2012: 37)

AGM 2008 (25 µg/L) 2009 (16 µg/L) 2010 (16 µg/L) Medium 2011 (17 µg/L) 2012 (26 µg/L) 2013 (29 µg/L) 2014 (17 µg/L) AGM 2008 (0.03 mg/L) 2009 (0.10 mg/L) 2010 (0.06 mg/L) Medium 2011 (0.05 mg/L) 2012 (0.06 mg/L) 2013 (0.07 mg/L) 2014 (0.07 mg/L)

ENRD10 (AAM) 2011 (0.35 mg/L) 2012 (0.57 mg/L) 2013 (0.54 mg/L) Medium 2014 (0.54 mg/L) 2015 (0.65 mg/L) 2016 (0.65 mg/L) 2017 (0.68 mg/L) 2018 (0.69 mg/L)

Medium 36/93

Medium 18/28

High 14/38

02/26/2015: Avg CofC - 1.4, FLEPPC - 56% 12/10/2015: Avg CofC - Medium 1.4, FLEPPC - 49% 10/31/2016: Avg CofC - 1.2, FLEPPC - 55%

Medium 16/33

High 34/176

Medium 19/102

Medium 46/66

Medium 6/12

High 138/184 High 23/124

Medium 11/45

Medium 10/12

Medium 107/312

High 139/228

ENRD10 (AAM) 2011 (1.02 mg/L) 2012 (0.84 mg/L) 2013 (0.97 mg/L) Medium 2014 (0.77 mg/L) 2015 (0.87 mg/L) 2016 (0.72 mg/L) 2017 (0.90 mg/L)

Low 10/16

Medium 217/345

Medium 22/64

Medium 16/27

High 108/253 ENRD10 (AAM) 2011 (0.59 mg/L) 2012 (0.74 mg/L) Medium 2013 (0.89 mg/L) 2014 (0.48 mg/L) 2015 (0.90 mg/L) 2016 (0.71 mg/L) ENRD10 (AAM) 2011 (0.36 mg/L) 2012 (0.56 mg/L) 2013 (0.52 mg/L) Medium 2014 (0.41 mg/L) 2015 (0.73 mg/L) 2016 (0.68 mg/L) 2017 (0.72 mg/L) 2018 (0.78 mg/L)

AGM Insufficient Data ENRD11 (AGM) 2011 (2.6 µg/L) 2013 (5.7 µg/L) 2015 (5.1 µg/L) 2016 (2.5 µg/L) 2017 (3.9 µg/L) ENRD12 (AGM) 2011 (5.3 µg/L) 2013 (5.6 µg/L) Medium 2014 (8.3 µg/L) 2015 (7.6 µg/L) 2016 (5.6 µg/L) 2017 (7.5 µg/L) ENRE1 (AGM) 2011 (5.4 µg/L) 2012 (6.4 µg/L) 2013 (3.8 µg/L) 2014 (6.6 µg/L) 2015 (5.8 µg/L) 2016 (3.8 µg/L) 2017 (5.1 µg/L)

ENRD11 (AGM) 2011 (0.01 mg/L) 2013 (0.24 mg/L) 2015 (0.37 mg/L) 2016 (0.35 mg/L) 2017 (0.68 mg/L) 2018 (0.43 mg/L) ENRD12 (AGM) 2011 (0.01 mg/L) 2013 (0.28 mg/L) 2014 (0.10 mg/L) Medium 2015 (0.16 mg/L) 2016 (0.38 mg/L) 2017 (0.70 mg/L) ENRE1 (AGM) 2011 (0.09 mg/L) 2012 (0.57 mg/L) 2013 (0.32 mg/L) 2014 (0.26 mg/L) 2015 (0.32 mg/L) 2016 (0.48 mg/L) 2017 (0.76 mg/L) Medium 11/22

High No Data

Low Impaired

2006 452/831

2002 (37.28 µg/L) Medium 2008 (20.65 µg/L)

LVI 21FLGW 40239 (22AUG2011: 17) 21FLWPB 28010465 Medium (06AUG2008: 39; 05NOV2013: 35) 21FLWPB 41841 (14NOV2012: 32) AGM 2008 (29 µg/L) 2009 (17 µg/L) 2010 (24 µg/L) Medium 2011 (28 µg/L) 2012 (30 µg/L) 2013 (36 µg/L) 2014 (28 µg/L)

AGM 2008 (0.07 mg/L) 2009 (0.10 mg/L) 2010 (0.08 mg/L) Medium 2011 (0.06 mg/L) 2012 (0.09 mg/L) 2013 (0.08 mg/L) 2014 (0.07 mg/L)

AGM 2008 (24 µg/L) 2009 (15 µg/L) 2010 (34 µg/L) Low 2011 (27 µg/L) 2012 (27 µg/L) 2013 (57 µg/L) 2014 (31 µg/L) 2002 (59.69 µg/L) 2010 2007 (23.78 µg/L) 2008 (23.73 µg/L)

2003 (31.25 µg/L) 2010 2008 (28.07 µg/L)

Medium 2010

2010 22/26

Medium

Low 8/28

Medium 2011

Medium 12/30

Medium 31/50

Medium 8/33

High 8/42

ENRE3 (AGM) 2015 (0.13 mg/L) Medium 2016 (0.19 mg/L) 2017 (0.44 mg/L) 2018 (0.65 mg/L)

High N/A

ENRE3 (AGM) 2015 (0.41 mg/L) Medium 2016 (0.50 mg/L) 2017 (0.46 mg/L) 2018 (0.40 mg/L) ENRE3 (AGM) 2015 (0.035 mg/L) Medium 2016 (0.048 mg/L) 2017 (0.051 mg/L) 2018 (0.045 mg/L)

Medium 12/25

ENRD13 (PCT) Medium 83/344

Medium 25/32

High 23/104

Medium 10/29

Medium 8/14

High 27/101

Medium 117/444

Medium 62/104

Low 117/310

Low Impaired

ENRE4 (AGM) 2011 (4.7 µg/L) 2012 (5.3 µg/L) 2013 (3.9 µg/L) Medium 2014 (5.3 µg/L) 2015 (5.3 µg/L) 2016 (4.3 µg/L) 2017 (4.7 µg/L) 2018 (4.8 µg/L) Medium 21/138

Medium 37/56

Medium 124/267

High 21/117

AGM (11 µg/L) 2011 (9 µg/L) 2012 (8 µg/L) 2013 (7 µg/L) 2014 (7 µg/L) 2015 (6 µg/L) 2016 (12 µg/L) 2017 (8 µg/L) 2018 (23 µg/L) Medium ENRE4 (AGM) 2011 (6.4 µg/L) 2012 (7.2 µg/L) 2013 (7.0 µg/L) 2014 (7.0 µg/L) 2015 (6.4 µg/L) 2016 (4.8 µg/L) 2017 (7.8 µg/L) 2018 (7.1 µg/L)

ENRE4 (AGM) 2011 (0.65 mg/L) 2012 (0.63 mg/L) 2013 (0.57 mg/L) Medium 2014 (0.57 mg/L) 2015 (0.52 mg/L) 2016 (0.58 mg/L) 2017 (0.78 mg/L) 2018 (0.65 mg/L)

ENRE4 (AGM) 2011 (0.044 mg/L) 2012 (0.035 mg/L) 2013 (0.040 mg/L) Medium 2014 (0.043 mg/L) 2015 (0.041 mg/L) 2016 (0.020 mg/L) 2017 (0.049 mg/L) 2018 (0.052 mg/L)

Medium

Low Medium 26/42

Low 12/28

Medium 2011

Medium 40/94

Medium 2011

Medium 12/42

High N/A

Medium 2011

Low 36/145

Low 32/235

Medium 62/149

Medium 117/433

Medium 57/269

Medium Medium NA

Medium 13/30

AGM 2011 (0.23 mg/L) 2012 (0.68 mg/L) Medium 2013 (0.33 mg/L) 2015 (0.43 mg/L) 2016 (0.34 mg/L) 2017 (0.51 mg/L)

Medium

AGM 2011 (52 µg/L) Medium 2016 (32 µg/L) 2017 (38 µg/L) 2018 (15 µg/L)

AGM 2011 (0.09 mg/L) Medium 2016 (0.14 mg/L) 2017 (0.07 mg/L) 2018 (0.09 mg/L)

Low 5/20

Low 9/10

Medium

Low

High 6/22

Medium 7/9 Medium 136/300

Medium Impaired

High NA

Medium 18/29

High

Medium

Medium 6/13

Annual Geometric Mean(s) 2008 (0.40 mg/L) 2009 (0.38 mg/L) Medium 2010 (0.37 mg/L) 2011 (0.43 mg/L) 2012 (0.43 mg/L) 2013 (0.39 mg/L)

Medium

Medium 2012

Low 17/91

Low Medium 18/23

Medium

Low Low

High

Low 24/24

Low 15/17

Low 11/19

Low 8/18

Medium 12/27

Low 9/51 Medium 6/6

High 3/4

Low N/A

Low 56/200

ENRV2 (AGM) 2011 (0.78 mg/L) 2012 (1.03 mg/L) 2013 (0.59 mg/L) Medium 2014 (0.80 mg/L) 2015 (0.76 mg/L) 2016 (0.78 mg/L) 2017 (0.86 mg/L) 2018 (0.83 mg/L) AGM 2011 (0.55 mg/L) 2013 (0.41 mg/L) Medium 2015 (0.48 mg/L) 2016 (0.70 mg/L) 2017 (0.78 mg/L)

High NA

High NA

High 1/5

High N/A

Low 16/72

High N/A

High 1/23 High N/A

Medium

SCI (n=4) WBID Mean (43) Medium Mean 1 (23), Mean 2 (53)

AGM 2012 (0.74 mg/L) 2013 (0.82 mg/L) 2014 (0.83 mg/L) Medium 2015 (0.81 mg/L) 2016 (0.81 mg/L) 2017 (0.78 mg/L) 2018 (0.78 mg/L) 2019 (0.85 mg/L)

Medium 5/17

High 7/22

Low 8/9

Low 9/42

Medium 5/5

High Medium 6/13

SCI (n=2) WBID Mean (37) Medium Mean 1 (39), Mean 2 (35)

AGM Medium 2011 (3.31 mg/L) 2012 (3.06 mg/L)

AGM Medium 2011 (0.20 mg/L) 2012 (0.19 mg/L)

Low 7/7

High 6/8

Medium 5/12

Medium 22/30

Medium 26/26 Beach Advisories 2012 (0 days) 2013 (0 days) 2014 (0 days) High 2015 (0 days) 2016 (0 days) 2017 (76 days) 2018 (no advisory) Beach Advisories 2012 (0 days) 2013 (no advisory) 2014 (no advisory) High 2015 (no advisory) 2016 (no advisory) 2017 (29 days) 2018 (no advisory)

Medium 5/22

High NA

Low N/A

Medium 30/82

Low N/A

Low 7/28

SCI (n=6) WBID Mean (49) Medium Mean 1 (26), Mean 2 (45)

AGM 2012 (0.93 mg/L) 2013 (1.10 mg/L) 2014 (0.97 mg/L) Medium 2015 (1.10 mg/L) 2016 (1.09 mg/L) 2017 (1.14 mg/L) 2018 (1.04 mg/L) 04/28/2009: 58.82% 10/07/2009: 27.27% Medium 04/05/2010: 23.81% 10/06/2010: 30.16% 04/06/2011: 44.44%

AGM 2013 (1.64 mg/L) Medium 2017 (2.24 mg/L) 2018 (1.85 mg/L)

High 16/61

Low 5/7

Medium 7/27

Low 14/66

Low

AGM 2011 (21 µg/L) Medium 2016 (14 µg/L) 2017 (22 µg/L) 2018 (11 µg/L)

AGM 2011 (0.89 mg/L) Medium 2016 (0.64 mg/L) 2017 (0.71 mg/L) 2018 (0.58 mg/L)

AGM 2011 (0.05 mg/L) Medium 2016 (0.04 mg/L) 2017 (0.04 mg/L) 2018 (0.03 mg/L)

Low 43/313 High N/A

High N/A

High N/A

ENRL4 (AGM) 2009 (3.7 µg/L) 2010 (3.1 µg/L) 2011 (2.8 µg/L) Medium 2012 (4.0 µg/L) 2013 (3.1 µg/L) 2014 (4.9 µg/L) 2015 (2.9 µg/L) 2016 (3.2 µg/L)

Medium 2012

High N/A

Low 13/77

High N/A

AGM 2015 (29 µg/L) Medium 2016 (23 µg/L) 2017 (41 µg/L)

AGM 2015 (0.05 mg/L) Medium 2016 (0.05 mg/L) 2017 (0.05 mg/L) LVI (n=3) WBID Mean (28) Medium Mean 1 (31), Mean 2 (16)

AGM 2016 (13 µg/L) Medium 2017 (6 µg/L) 2018 (9 µg/L)

AGM 2016 (0.66 mg/L) Medium 2017 (0.46 mg/L) 2018 (0.56 mg/L)

AGM 2016 (0.03 mg/L) Medium 2017 (0.02 mg/L) 2018 (0.02 mg/L)

Low 12/20

Low 8/13

Low 11/18

SCI (n=2) WBID Mean (28) Medium Mean 1 (30), Mean 2 (27) Medium 8/24

06/30/2015: 0% Medium 02/23/2016: 67% 10/31/2017: 58%

AGM 2011 (0.09 mg/L) Medium 2015 (0.20 mg/L) 2016 (0.12 mg/L) 2017 (0.19 mg/L)

04/29/2009: 68.42% 04/30/2009: 15.63% Medium 10/06/2009: 40% 10/06/2009: 17.65%

AGM (11 µg/L) 2016 (0 µg/l) ENRH3 (AGM) 2009 (0.4 µg/L) 2010 (0.4 µg/L) 2011 (0.4 µg/L) 2012 (0.3 µg/L) 2013 (0.5 µg/L) 2014 (0.7 µg/L) 2015 (0.8 µg/L) 2016 (0.8 µg/L) ENRH4 (AGM) 2010 (0.5 µg/L) Medium 2011 (0.3 µg/L) 2012 (0.2 µg/L) 2013 (0.4 µg/L) 2014 (0.7 µg/L) 2015 (0.8 µg/L) ENRH6 (AGM) 2009 (0.2 µg/L) 2010 (0.4 µg/L) 2011 (0.4 µg/L) 2012 (0.3 µg/L) 2013 (0.4 µg/L) 2014 (0.4 µg/L) 2015 (0.4 µg/L)

Medium

Medium

Medium Medium Medium Medium Medium Medium Medium 6/24

Medium

High 7/32

Low 16/27

Medium 7/12

AGM Medium 2016 (11 µg/L) 2017 (7 µg/L)

AGM Medium 2016 (0.61 mg/L) 2017 (0.59 mg/L)

AGM Medium 2016 (0.03 mg/L) 2017 (0.02 mg/L)

AGM 2011 (59 µg/L) Medium 2012 (41 µg/L) 2013 (10 µg/L) 2017 (74 µg/L)

AGM 2011 (0.12 mg/L) Medium 2013 (0.10 mg/L) 2017 (0.17 mg/L)

Low vp=7/11

Low

Low

ENRM3: AGM 2008 (4.0 µg/L) Medium 2009 (3.2 µg/L) 2013 (3.3 µg/L) ENRM3: AGM 2008 (0.27 mg/L) 2009 (0.29 mg/L) 2010 (0.25 mg/L) Medium 2011 (0.23 mg/L) 2012 (0.34 mg/L) 2013 (0.38 mg/L) 2014 (0.29 mg/L) 2015 (0.30 mg/L) 2002 (49 days) 2003 (215 days) 2004 (214 days) High 2005 (302 days) 2006 (34 days) 2007 (106 days) 2008 (14 days)

High N/A

Low 22/85

Low vp=38/136

High 12/15

Low vp=208/401

Medium 2009

Low 7/24

Low 7/7

ENRM1: AGM Medium 2008 (6.0 µg/L) 2009 (4.3 µg/L)

Medium 2012

Low vp=7/15 Medium 17/18

Low 6/21

Low 7/10

2002 (N/A) 2003 (69 days) 2004 (28 days) High 2005 (49 days) 2006 (7 days) 2007 (35 days) 2008 (14 days) AGM 2011 (31 µg/L) 2012 (26 µg/L) 2013 (14 µg/L) Medium 2014 (11 µg/L) 2015 (9 µg/L) 2016 (18 µg/L) 2017 (11 µg/L) AGM 2011 (1.25 mg/L) 2012 (1.27 mg/L) 2013 (0.71 mg/L) Medium 2014 (1.18 mg/L) 2015 (0.61 mg/L) 2016 (0.77 mg/L) 2017 (0.71 mg/L) AGM 2011 (0.06 mg/L) 2012 (0.05 mg/L) 2013 (0.05 mg/L) Medium 2014 (0.05 mg/L) 2015 (0.03 mg/L) 2016 (0.02 mg/L) 2017 (0.05 mg/L)

Low 5/20

High 7/7 High 9/14

Medium 2009

Low vp=137/1001

ENRM9: AGM 2008 (0.50 mg/L) 2009 (0.74 mg/L) 2010 (0.61 mg/L) Medium 2011 (0.66 mg/L) 2012 (1.40 mg/L) 2013 (1.25 mg/L) 2014 (0.48 mg/L) 2015 (0.33 mg/L)

ENRM9: AGM 2008 (0.025 mg/L) 2009 (0.036 mg/L) 2010 (0.026 mg/L) Medium 2011 (0.030 mg/L) 2012 (0.058 mg/L) 2013 (0.051 mg/L) 2014 (0.011 mg/L) 2015 (0.009 mg/L) 2002 (15 days) 2003 (14 days) 2004 (21 days) High 2005 (20 days) 2006 (14 days) 2007 (21 days) 2008 (7 days)

Medium 2009

Beach Advisories 2008 (No Advisories) 2009 (No Advisories) 2010 (No Advisories) High 2011 (No Advisories) 2012 (39 days) 2013 (78 days) 2014 (34 days) 2015 (41 days)

Medium N/A 11µg/L Annual Geometric Mean(s) Insufficient Data ENRM7: AGM Medium 2008 (3.2 µg/L) 2009 (3.6 µg/L) 2013 (1.7 µg/L) 2014 (2.8 µg/L) ENRM7: AGM 2008 (0.27 mg/L) 2009 (0.30 mg/L) 2010 (0.29 mg/L) Medium 2011 (0.25 mg/L) 2012 (0.37 mg/L) 2013 (0.53 mg/L) 2014 (0.33 mg/L) 2015 (0.30 mg/L)

Medium N/A

Low Impaired

ENRM7: AGM 2008 (0.38 mg/L) 2009 (0.45 mg/L) 2010 (0.37 mg/L) Medium 2011 (0.28 mg/L) 2012 (0.34 mg/L) 2013 (0.51 mg/L) 2014 (0.39 mg/L) 2015 (0.35 mg/L) 2002 (N/A) 2003 (7 days) 2004 (14 days) High 2005 (20 days) 2006 (35 days) 2007 (6 days) 2008 (0 days)

Medium 56/370

11µg/L Annual Geometric Mean(s) 2008 (5 µg/L) 2009 (4 µg/L) Medium ENRM4: AGM 2008 (6.5 µg/L) 2009 (10.9 µg/L) 2013 (4.9 µg/L) ENRM4: AGM 2008 (0.62 mg/L) 2009 (0.62 mg/L) 2010 (0.59 mg/L) Medium 2011 (0.36 mg/L) 2012 (0.47 mg/L) 2013 (0.60 mg/L) 2014 (0.49 mg/L) 2015 (0.46 mg/L)

Annual Geometric Mean(s) Medium 2008 (1.77 mg/L) 2009 (1.80 mg/L)

Annual Geometric Mean(s) Medium 2008 (0.15 mg/L) 2009 (0.15 mg/L)

Medium 34/144

Annual Geometric Mean(s) 2008 (3.01 mg/L) Medium 2009 (2.53 mg/L) 2010 (2.40 mg/L) 2011 (2.02 mg/L)

Low 13/26

High 3 / 6

Low 10/15

03/10/2011: 30% Medium 07/13/2017: 53%

High 36/282 Low 9/20

Beach Advisories 2009 (no advisory) 2010 (no advisory) 2011 (no advisory) High 2012 (28 days) 2013 (53 days) 2014 (27 days) 2015 (21 days) Beach Advisories 2008 (7 days) 2009 (0 days) 2010 (0 days) High 2011 (20 days) 2012 (41 days) 2013 (22 days) 2014 (13 days) 2015 (13 days) 2002 (0 days) 2003 (14 days) 2004 (21 days) High 2005 (0 days) 2006 (0 days) 2007 (21 days) 2008 (0 days) 2002 (0 days) 2003 (14 days) 2004 (14 days) High 2005 (22 days) 2006 (7 days) 2007 (22 days) 2008 (28 days) Beach Advisories 2008 (0 days) 2009 (0 days) 2010 (0 days) High 2011 (0 days) 2012 (9 days) 2013 (27 days) 2014 (1 day) 2015 (0 days)

Beach Advisories 2008 (0 days) 2009 (0 days) 2010 (0 days) High 2011 (0 days) 2012 (29 days) 2013 (16 days) 2014 (1 day) 2015 (6 days)

Beach Advisories 2008 (0 days) 2009 (0 days) 2010 (0 days) High 2011 (0 days) 2012 (38 days) 2013 (37 days) 2014 (8 days) 2015 (8 days) Beach Advisories 2008 (0 days) 2009 (0 days) 2010 (0 days) High 2011 (0 days) 2012 (36 days) 2013 (15 days) 2014 (2 days) 2015 (0 days)

Medium 2009

Beach Advisories 2008 (8 days) 2009 (0 days) 2010 (7 days) High 2011 (70 days) 2012 (7 days) 2013 (20 days) 2014 (13 days) 2015 (0 days)

Medium 2009

Beach Advisories 2008 (0 days) 2009 (0 days) 2010 (15 days) HIgh 2011 (21 days) 2012 (0 days) 2013 (No Advisories) 2014 (No Advisories) 2015 (No Advisories)

Beach Advisories 2008 (0 days) 2009 (7 days) 2010 (0 days) High 2011 (0 days) 2012 (32 days) 2013 (17 days) 2014 (0 days) 2015 (0 days)

Beach Advisories 2008 (0 days) 2009 (7 days) 2010 (0 days) High 2011 (31 days) 2012 (18 days) 2013 (17 days) 2014 (0 days) 2015 (0 days)

Beach Advisories 2008 (0 days) 2009 (7 days) 2010 (0 days) High 2011 (0 days) 2012 (60 days) 2013 (14 days) 2014 (0 days) 2015 (0 days) Beach Advisories 2008 (7 days) 2009 (7 days) 2010 (0 days) High 2011 (49 days) 2012 (0 days) 2013 (No Advisories) 2014 (No Advisories) 2015 (No Advisories)

Beach Advisories 2012 (0 days) 2013 (0 days) 2014 (0 days) High 2015 (21 days) 2016 (0 days) 2017 (0 days) 2018 (no advisory)

High NA

High

High

Low NA

ENRX13 (AGM) 2011 (0.41 mg/L) 2012 (0.71 mg/L) 2013 (0.47 mg/L) Medium 2014 (0.45 mg/L) 2015 (0.54 mg/L) 2016 (0.56 mg/L) 2017 (0.53 mg/L) 2018 (0.53 mg/L) ENRX13 (AGM) 2015 (0.46 mg/L) Medium 2016 (0.48 mg/L) 2017 (0.42 mg/L) 2018 (0.45 mg/L)

High N/A

ENRX14 (AGM) 2015 (8.3 µg/L) Medium 2016 (6.0 µg/L) 2017 (6.1 µg/L) ENRX14 (AGM) 2015 (0.69 mg/L) Medium 2016 (0.60 mg/L) 2017 (0.65 mg/L) ENRX14 (AGM) 2015 (0.036 mg/L) Medium 2016 (0.032 mg/L) 2017 (0.029 mg/L)

High NA

Low

Low Impaired

High NA

ENRV3 (AGM) 2013 (5.2 µg/L) Medium 2014 (5.2 µg/L) 2015 (3.7 µg/L) 2016 (2.9 µg/L)

ENRV3 (AGM): Station 21FLWQA 34SEAS110 Medium 2014 (0.72) (2015 (0.86) 2016 (0.73)

Low N/A

Low 173/1233

Low N/A

ENRW3 (AGM) 2015 (1.0 µg/L) Medium 2016 (2.6 µg/L) 2017 (0.6 µg/L)

ENRW3 (AGM) 2015 (0.36 mg/L) Medium 2016 (0.64 mg/L) 2017 (0.58 mg/L) High

ENRW11 (AGM) 2015 (0.41 mg/L) Medium 2016 (0.63 mg/L) 2017 (0.59 mg/L) Beach Advisories 2008 (5 days) 2009 (0 days) 2010 (0 days) High 2011 (27 days) 2012 (5 days) 2013 (0 days) 2014 (1 day) 2015 (0 days)

ENRE2 (AGM) Medium 2017 (0.43 mg/L) 2018 (0.37 mg/L)

ENRE2 (AGM) Medium 2015 (0.29 mg/L) 2017 (0.31 mg/L)

2008 (12 µg/L) Medium 2009 (18 µg/L) 2010 (22 µg/L)

Medium 13/36

ENRG1 (AGM) 2016 (0.26 mg/L) 2017 (0.32 mg/L) ENRG2 (AGM) 2016 (0.34 mg/L) 2017 (0.26 mg/L) ENRG3 (AGM) Medium 2016 (0.25 mg/L) 2017 (0.26 mg/L) ENRG4 (AGM) 2016 (0.29 mg/L) 2017 (0.23 mg/L) ENRG6 (AGM) Insufficient Data

High

High

High ENRG3 (AGM) 2016 (0.28 mg/L) 2017 (0.25 mg/L) Medium ENRG6 (AGM) 2016 (0.23 mg/L) 2017 (0.25 mg/L)

Medium 11/38

Medium 11/43

Low

ENRG3 (AGM) 2016 (0.33 mg/L) 2017 (0.23 mg/L) Medium ENRG6 (AGM) 2016 (0.28 mg/L) 2017 (0.23 mg/L)

High

2004 (14 days) 2005 (59 days) 2006 (8 days) High 2007 (7 days) 2008 (21 days) 2009 (15 days) 2010 (14 days) ENRG6 (AGM) 2015 (0.23 mg/L) Medium 2016 (0.24 mg/L) ENRG7 (AGM) No Data

Low

Low 7/20

High N/A

Medium 2009

Low 5/11

Medium 14/18 Medium 8/10

Low

Low 8/29

Low Impaired

Low 9/15

High 9/20

Low

Low Impaired

Medium 2012

Medium 2012

Medium 2012

High

Low vp=17/61

Low

High 7/22

Low 5/10

Medium 5/8

Assessment based on Medium DOH Fish Tissue Studies Low Comments

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is listed as impaired for this parameter because the shellfish harvesting classification is not fully approved by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture and Consumer Services. This parameter is being added to the Verified List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in the most recent consecutive three year period. This parameter is being added to the 303(d) List.

This parameter exceeds the listing threshold and will be added to the 303(d) List.

Beach advisories > 21 days/yr for 2001, 2002, and 2003.

Beach advisories > 21 days/yr for 2002 and 2003.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in the most recent consecutive three year period. This parameter is being added to the 303(d) List.

Beach advisories > 21 days/yr for 2002 and 2003.

PP = 270 / 2799; VP = 73 / 1188. This WBID was listed because there was a downgrade in the shellfish harvesting classification for some portion of this Class II waterbody.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in the most recent consecutive three year period. This parameter is being added to the 303(d) List.

Beach advisories > 21 days/yr for 2002 and 2003.

Listed based on shellfish harvesting classification of conditionally approved by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in the most recent consecutive three year period. This parameter is being added to the 303(d) List. This waterbody is listed as impaired for this parameter because the shellfish harvesting classification is not fully approved by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture and Consumer Services. This parameter is being added to the Verified List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in the most recent consecutive three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This parameter exceeds the listing threshold and will be added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

Listed based on shellfish harvesting classification of prohibited by Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture.

This parameter exceeds the listing threshold and will be added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

PP = 4 / 17; VP = 6 / 20

This parameter exceeds the listing threshold and will be added to the 303(d) List. This parameter exceeds the listing threshold and will be added to the 303(d) List. WBID name was changed from Direct Runoff to Bay to match the 1998 303(d) list name. This parameter exceeds the listing threshold and will be added to the 303(d) List. This parameter exceeds the listing threshold and will be added to the 303(d) List. This parameter exceeds the listing threshold and will be added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a) F.A.C. This parameter will be added to the 303(d) List.

This parameter exceeds the listing threshold and will be added to the 303(d) List.

DO met the listing threshold and the causative pollutant is total nitrogen. There are low urban and built up (0.06%) and 70.39% upland forest land uses.

This parameter exceeds the listing threshold and will be added to the 303(d) List. This waterbody is listed as impaired for this parameter because the shellfish harvesting classification is not fully approved by the Shellfish Harvest Area Classification Program of the department of Agriculture and Consumer Services. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is listed as impaired for this parameter because the shellfish harvesting classification is not fully approved by the Shellfish Harvest Area Classification Program of the department of Agriculture and Consumer Services. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This parameter exceeds the listing threshold and will be added to the 303(d) List. This parameter is impaired because the shellfish harvesting classification is not fully approved by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture and Consumer Services. This parameter is being added to the 303(d) list. This parameter exceeds the listing threshold and will remain on the 303(d) List. EPA established TMDL 3/30/01. This parameter is impaired because the shellfish harvesting classification is not fully approved by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture and Consumer Services. This parameter is being added to the 303(d) list. This parameter is impaired for this waterbody. The waterbody includes at least one sampling location that has a median fecal coliform MPN value that exceeds 14 counts per 100 ml for the verified period. This parameter is being added to the 303(d) list. This parameter is impaired because the shellfish harvesting classification is not fully approved by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture and Consumer Services. This parameter is being added to the 303(d) list. Listed based on change in shellfish harvesting classification (downgraded from unclassified to prohibited). Listed based on change in shellfish harvesting classification (downgraded from approved to conditionally restricted).

This waterbody is listed as impaired for this parameter because the shellfish harvesting classification is not fully approved by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture and Consumer Services. This parameter is being added to the Verified List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in the most recent consecutive three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter because there were 21 days or more of beach advisories in 2012. This is a beach WBID, which are assessed solely on beach advisory information received from DOH.^ This parameter is being added to the 303(d) List.

Beach advisories > 21 days/yr for 2001, 2002, and 2003 Listed based on shellfish harvesting classification of prohibited in summer and winter by Shellfish Environmental Assessment Section (SEAS).

Listed based on shellfish harvesting classification of prohibited in summer and winter by Shellfish Environmental Assessment Section (SEAS).

Listed based on change in shellfish harvesting classification (downgraded from approved to conditionally restricted).

Waterbody did not meet water quality standards

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. However, the impairment may be due to natural conditions; therefore, the assessment is pending further analysis by DEP. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

Listed based on change in shellfish harvesting classification (downgraded from conditionally approved to conditionally restricted).

PP - 461/2047 Potentially Impaired VP - 150/900 Verified Impaired

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is listed as impaired for this parameter because the shellfish harvesting classification is not fully approved by the Shellfish Harvest Area Classification Program of the Department of Agriculture and Consumer Services. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is listed as impaired for this parameter because the shellfish harvesting classification is not fully approved by the Shellfish Harvest Area Classification Program of the Department of Agriculture and Consumer Services. Additionally, fecal coliform water quality data also indicate a bacteria problem in the current assessment period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

Listed based on shellfish harvesting classification of conditionally approved and conditionally restricted in summer and conditionally restricted in winter by Shellfish Environmental Assessment Section (SEAS).

This waterbody is listed as impaired for this parameter because the shellfish harvesting classification is not fully approved by the Shellfish Harvest Area Classification Program of the Department of Agriculture and Consumer Services. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

Listed based on shellfish harvesting classification of prohibited in summer and winter by Shellfish Environmental Assessment Section (SEAS).

Listed based on shellfish harvesting classification of prohibited in summer and winter by Shellfish Environmental Assessment Section (SEAS).

Listed based on shellfish harvesting classification of conditionally restricted in summer and winter by Shellfish Environmental Assessment Section (SEAS). Per photographs showing an abundance of invasive plant species on Huckleberry Creek. Listed based on change in shellfish harvesting classification (downgraded from unclassified to prohibited).

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

PP = 2 / 2; VP = 9 / 24

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and will remain on the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and will remain on the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody remains impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a high color lake more than once in a three year period. This parameter will remain on the Verified List and the 303(d) List.

This waterbody remains impaired for this parameter based on information indicating total nitrogen is causing or contributing to the nutrient impairment of the waterbody. This parameter will remain on the Verified List and the 303(d) List.

This waterbody remains impaired for this parameter based on information indicating total phosphorus is causing or contributing to the nutrient impairment of the waterbody. This parameter will remain on the Verified List and the 303(d) List.

This waterbody remains impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a high color lake more than once in a three year period. This parameter will remain on the Verified List and the 303(d) List. This waterbody remains impaired for this parameter based on information indicating total nitrogen is causing or contributing to the nutrient impairment of the waterbody. This parameter will remain on the Verified List and the 303(d) List.

This waterbody remains impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a high color lake more than once in a three year period. This parameter will remain on the Verified List and the 303(d) List.

This waterbody remains impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a high color lake more than once in a three year period. This parameter will remain on the Verified List and the 303(d) List.

This waterbody remains impaired for this parameter based on information indicating total nitrogen is causing or contributing to the nutrient impairment of the waterbody. This parameter will remain on the Verified List and the 303(d) List.

This waterbody remains impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a high color lake more than once in a three year period. This parameter will remain on the Verified List and the 303(d) List.

PP = 2 / 2; VP = 20 / 20

This waterbody is impaired for this parameter based on the number of exceedances for the sample size, and anthropogenic sources have been identified using genetic marker and chemical tracer data. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter based on the number of exceedances for the sample size, and anthropogenic sources have been identified using genetic marker and chemical tracer data. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62-303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody was placed in category 4c in the previous assessment cycle, but EPA deferred action on approving the assessment to allow for additional review.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

Exceeds the 14 #/100 mL criterion.

This parameter is impaired because the shellfish harvesting classification is not fully approved by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture and Consumer Services. It is being added to the 303(d) list.

This canal was verified as impaired for nutrients because the annual average chlorophyll-a values exceeded 11 µg/l in 2009. Nitrogen and phosphorus are the limiting nutrients based on a median TN/TP ratio of 13 (n=104).

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and nutrients have been identified as the causative pollutant. This parameter will remain on the 303(d) List.

This waterbody is impaired for this parameter based on failing linear vegetation survey results. This parameter is being added to the 303(d) List.

This spring has been verified as impaired for nutrients based on "other information" that indicated an imbalance in flora or fauna. It is included in a springs report "Florida Springs Initiative Monitoring Network Report 2008" that documents nutrient enrichment is apparent due to abundant algae documented through photography as well as bioassessment methods. Nitrate+nitrite levels range from 0.56 - 0.8 mg/L during the verified period and is the likely cause of the impairment; however, in accordance with Rule 62- 303.710(4), F.A.C., the limiting nutrients are nitrogen and phosphorus based on a median TN/TP ratio of 14 (n=17).

This waterbody is impaired for this parameter. The annual geometric mean exceeded the criterion more than once in a three-year period. This parameter is being added to the 303(d) List.

This spring is included in a springs report "Florida Springs Initiative Monitoring Network Report 2008". The report documents that nutrient enrichment is apparent due to elevated nitrate levels, which range from 0.2 - 0.5 mg/L, and Rapid Peryphiton Survey information that indicate an imbalance of algae; therefore this waterbody is being added to the Verified list. This waterbody is impaired for this parameter. The annual geometric mean exceeded the criterion more than once in a three-year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and Nutrients has been identified as the causative pollutant. This parameter is being added to the 303(d) List. Dissolved oxygen grab samples used in this analysis were assessed against a time of day adjustment as described in Rule 62-303.420(9), F.A.C.

This waterbody is impaired for this parameter. The annual geometric mean exceeded the nutrient criteria more than once in a three-year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric mean exceeded the nutrient criteria more than once in a three-year period. This parameter is being added to the 303(d) List.

This parameter is impaired because the shellfish harvesting classification is not fully approved by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture and Consumer Services. It is being added to the 303(d) list. This parameter is impaired because the shellfish harvesting classification is not fully approved by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture and Consumer Services. It is being added to the 303(d) list.

This waterbody is impaired for this parameter. The annual geometric means exceeded the criterion more than once in a three-year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the criterion more than once in a three-year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

pp = 144 / 758; vp = 108 / 508

Exceeds the 14 #/100 mL criterion.

This parameter is impaired because the shellfish harvesting classification is not fully approved by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture and Consumer Services. It is being added to the 303(d) list. This waterbody is impaired for this parameter based on failing rapid periphyton survey results. There are at least two temporally independent samples greater than 25% and this parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on failing linear vegetation survey results. This parameter is being added to the 303(d) List.

This spring has been verified as impaired for nutrients based on "other information" that indicated an imbalance in flora or fauna. It is included in a springs report "Florida Springs Initiative Monitoring Network Report 2008" that documents nutrient enrichment is apparent due to abundant algae documented through photography as well as bioassessment methods. Nitrate+nitrite levels range from 0.14 - 1.4 mg/L during the verified period and is the likely cause of the impairment; however, in accordance with Rule 62- 303.710(4), F.A.C., the limiting nutrient is phosphorus based on a median TN/TP ratio of 44 (n=69).

This waterbody is impaired for this parameter. The annual geometric mean exceeded the criterion more than once in a three-year period. This parameter is being added to the 303(d) List.

This parameter is listed as impaired because the shellfish harvesting classification is not fully approved by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture. This parameter is being added to the 303(d) list.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Station 21FLSEAS37SEAS090 (Salt River at Hwy 44 Bridge) had a median value that exceeded the 14 counts/100 mL criterion with at least 20 samples in the verified period. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

This waterbody is listed as impaired for this parameter because the shellfish harvesting classification is not fully approved by the Shellfish Harvest Area Classification Program of the department of Agriculture and Consumer Services. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

This parameter is listed as impaired because the shellfish harvesting classification is not fully approved by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture. This parameter is being added to the 303(d) list.

This spring has been verified as impaired for nutrients based on "other information" that indicated an imbalance in flora or fauna. It is included in a springs report "Florida Springs Initiative Monitoring Network Report 2008" that documents nutrient enrichment is apparent due to abundant algae documented through photography as well as bioassessment methods. Nitrate+nitrite levels range from 0.25 - 1.4 mg/L during the verified period and is the likely cause of the impairment; however, in accordance with Rule 62- 303.710(4), F.A.C., the limiting nutrients are nitrogen and phosphorus based on a median TN/TP ratio of 23 (n=17). This waterbody is impaired for this parameter. The annual geometric mean exceeded the criterion more than once in a three-year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric mean exceeded the criterion more than once in a three-year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on samples with greater than 25% algal coverage and although two results were less than or equal to 25% percent coverage, the dominant taxa of the algal community include taxa known to indicate nutrient enrichment. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on failing linear vegetation survey results. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on failing bioassessments and nutrients have been determined to be the causative pollutant. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric mean exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric mean exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric mean exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

pp = 19 / 31 Potentially Impaired; vp = 24 / 25 Impaired. DO met the verification threshold and TN was identified as the causative pollutant. 11 TN measurements, median 2.04 mg/L. 15 TP measurements, median 0.05 mg/L, 11 BOD measurements, median 0.8 mg/L. This waterbody is impaired for this parameter. The annual geometric mean exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric mean exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric mean exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

PP = 0 / 4, Insufficient data; VP = 7 / 31, Impaired. Fecal coliform mean 1169 counts/100mL, Median 260 counts/100 mL, range 2 - 20,000 counts/100mL.

This parameter is impaired for this waterbody based on "other information" that indicated an imbalance in flora or fauna. It is included in a springs report "Florida Springs Initiative Monitoring Network Report and Recognized Sources of Nitrate, February 2010" that documents nutrient enrichment is apparent due to abundant algae documented through photography as well as bioassessment methods. This parameter will be added to the 303(d) list.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. However, the impairment may be due to natural conditions; therefore, the assessment is pending further analysis by DEP.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on failing linear vegetation surveys with an average C of C score < 2.5 and FLEPPC percent coverage of > 25%. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter. The annual geometric mean exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric mean exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a) F.A.C. This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter based on the number of exceedances for the sample size.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the annual geometric means exceeding the criterion more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the annual geometric means exceeding the criterion more than once in a three year period. This parameter is being added to the 303(d) List.

Verified Impaired with 41 exceedances out of 123 samples.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a high color lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size. Median total nitrogen and total phosphorus values were not elevated relative to comparable waters and biochemical oxygen demand was identified as the causative pollutant because it was elevated relative to comparable waters (exceeded 2.0 mg/L). This parameter is being added to the 303(d) list.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a high color lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear acidic lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear acidic lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear acidic lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on failing bioassessments and nutrients have been determined to be the causative pollutant. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear acidic lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear acidic lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear acidic lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter based on failing bioassessments and nutrients have been determined to be the causative pollutant. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric mean exceeded the nutrient criteria more than once in a three-year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric mean exceeded the nutrient criteria more than once in a three-year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric mean exceeded the nutrient criteria more than once in a three-year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on failing linear vegetation survey results. This parameter is being added to the 303(d) List. Data from outside the verified period was used to support this assessment.

This waterbody is verified as impaired for dissolved oxygen based on the number of exceedances. Total nitrogen has been identified as the causative pollutant.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear acidic lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear acidic lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear acidic lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on failing bioassessments and nutrients have been determined to be the causative pollutant. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear acidic lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear acidic lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear acidic lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a high color lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on failing bioassessments and nutrients have been determined to be the causative pollutant. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. Pinellas County provided additional biological data used in this assessment.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a high color lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody was previously assessed as impaired for Nutrients (TSI), however that parameter is no longer assessed to determine impairment per Rule 62-303, F.A.C.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody was previously impaired for Nutrients (TSI), however that parameter is no longer being assessed to determine impairment. This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody was previously assessed as impaired for Nutrients (TSI), however that parameter is no longer assessed to determine impairment per Rule 62-303, F.A.C.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody was previously impaired for Nutrients (TSI), however that parameter is no longer being assessed to determine impairment.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody was previously assessed as impaired for Nutrients (TSI), however that parameter is no longer assessed to determine impairment per Rule 62-303, F.A.C.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody was previously impaired for Nutrients (TSI), however that parameter is no longer being assessed to determine impairment.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody was previously assessed as impaired for Nutrients (TSI), however that parameter is no longer assessed to determine impairment per Rule 62-303, F.A.C.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody was previously impaired for Nutrients (TSI), however that parameter is no longer being assessed to determine impairment.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody was previously impaired for Nutrients (TSI), however that parameter is no longer being assessed to determine impairment. This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a) F.A.C. This parameter is being added to the 303(d) List.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size and is being added to the 303(d) list.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a) F.A.C. This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter based on the number of exceedances for the sample size and nutrients have been identified as the causative pollutant. Samples used in this assessment were evaluated against a time of day adjustment as described in 62-303.420(9), F.A.C. This parameter is being added to the Verified List and will remain on the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a high color lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a high color lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a high color lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on failing bioassessments and nutrients have been determined to be the causative pollutant. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear acidic lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. PP - 4/8 Insufficient data; VP - 13/20 Verified impaired.

Impaired based on the number of exceedances.

This waterbody is impaired for this parameter based on failing linear vegetation survey results. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on failing bioassessments and nutrients have been determined to be the causative pollutant. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody was previously assessed as impaired for Nutrients (TSI), however that parameter is no longer assessed to determine impairment per Rule 62-303, F.A.C.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody was previously impaired for Nutrients (TSI), however that parameter is no longer being assessed to determine impairment.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody was previously impaired for Nutrients (TSI), however that parameter is no longer being assessed to determine impairment.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. Through correspondence with Polk County, It was determined that the TKN and TP samples collected at station 21FLPOLKSADDLE CRK PK Y on 10/07/2010 are not considered to be representative of the waterbody as a whole. Polk County has informed the department that they will remove these samples from Florida STORET. Because data had already been extracted for IWR Run 52 upon which Group 3 Cycle 3 assessments are based, the department manually excluded the unrepresentative data for the time being and recalculated the TN and TP AGM’s for WBID 1497J. This exclusion did not change the assessment status of TN or TP for Cycle 3.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. Through correspondence with Polk County, It was determined that the TKN and TP samples collected at station 21FLPOLKSADDLE CRK PK Y on 10/07/2010 are not considered to be representative of the waterbody as a whole. Polk County has informed the department that they will remove these samples from Florida STORET. Because data had already been extracted for IWR Run 52 upon which Group 3 Cycle 3 assessments are based, the department manually excluded the unrepresentative data for the time being and recalculated the TN and TP AGM’s for WBID 1497J. This exclusion did not change the assessment status of TN or TP for Cycle 3. This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.390(2)(f) F.A.C. There is a DEP Adopted Fecal Coliform TMDL for this waterbody. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a) F.A.C. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on failing bioassessments and nutrients have been determined to be the causative pollutant. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient threshold more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient threshold more than once in a three year period. This parameter is being added to the 303(d) List.

Impaired based on the number of exceedances.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody was previously assessed as impaired for Nutrients (TSI), however that parameter is no longer assessed to determine impairment per Rule 62-303, F.A.C. This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody was previously impaired for Nutrients (TSI), however that parameter is no longer being assessed to determine impairment.

This waterbody is impaired for this parameter. The annual geometric mean exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric mean exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody was previously impaired for Nutrients (TSI), however that parameter is no longer being assessed to determine impairment.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a high color lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric mean exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a) F.A.C. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

pp = 83 / 120; vp = 69 / 81. Verified impaired. Nutrients (total nitrogen) and BOD were identified as the causative pollutants based on Chl-a data/nutrient impairment. Verified period median TN = 1.41 mg/L (90 values), median TP = 0.15 mg/L (93 values), median BOD = 3.0 mg/L (91 values). EPA developed and proposed TMDL in September 2004. In Cycle 1 the WBID name was Rocky Creek. This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using chemical tracer data and land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Station 21FLHILL102 (Channel A at SR 580 bridge) had a median value that exceeded the 14 counts/100 mL criterion with at least 20 samples in the verified period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

pp = 71 / 350; vp = 49 / 231 Verified impaired. Nutrients were identified as the causative pollutant based on Chl-a data/nutrient impairment verification.

pp = Potentially impaired; vp = Verified impaired. Annual average Chl-a values exceeded 11 µg/l in 1999 - 2005, and values were 27.9, 32.44, 30.02, 22.67, 49.07, 38.14 and 45.29 µg/l, respectively. For the historical listing, annual average Chl-a values in the verified period exceeded the minimum historical annual average value of 21.12 µg/l for 1990-1994 by more than 50% in 2004 (38.14 µg/l), and 2005 (45.28 µg/l). Nitrogen is the limiting nutrient based on a median TN/TP ratio of 3.16 (133 values). The verified period total nitrogen median = 1.665 (134 values), total phosphorus median = 0.59 mg/l (150 values), and the BOD median = 3.25 mg/l (106 values).

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. There is a DEP Adopted - EPA Approved Fecal Coliform TMDL for this waterbody and therefore, the priority for TMDL Development is Low.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size. Total nitrogen and total phosphorus were identified as causative pollutants because they were elevated relative to comparable reference condition waters (exceeded 1.7 mg/L for TN and 0.12 for TP). This parameter will be added to the 303(d) list.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size and is being added to the 303(d) list.

This parameter is impaired for this waterbody because the annual average chlorophyll-a values exceeded 20 µg/l in 2007 and 2008. Based on the median TN/TP ratio of 2, total nitrogen is the limiting nutrient. This parameter is being added to the 303(d) list. This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in a three-year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in a three-year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody was previously assessed as impaired for Nutrients (TSI), however that parameter is no longer assessed to determine impairment per Rule 62-303, F.A.C.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody was previously impaired for Nutrients (TSI), however that parameter is no longer being assessed to determine impairment.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in a three-year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. There is a DEP Adopted Fecal Coliform TMDL for this waterbody. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size and is being added to the 303(d) list.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a) F.A.C. This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody was previously assessed as impaired for Nutrients (TSI), however that parameter is no longer assessed to determine impairment per Rule 62-303, F.A.C.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody was previously impaired for Nutrients (TSI), however that parameter is no longer being assessed to determine impairment.

Impaired with total phosphorus and biochemical oxygen demand identified as the causative pollutants.

Impaired based on the number of exceedances.

This waterbody is impaired because annual average Chl-a values exceeded 20 µg/l in 2008. Nitrogen and phosphorus are the limiting nutrients based on a median TN/TP ratio of 10.04 (n=23).

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric mean exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody was previously assessed as impaired for Nutrients (TSI), however that parameter is no longer assessed to determine impairment per Rule 62-303, F.A.C. This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody was previously impaired for Nutrients (TSI), however that parameter is no longer being assessed to determine impairment.

This waterbody is impaired for this parameter. The annual geometric mean exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody was previously impaired for Nutrients (TSI), however that parameter is no longer being assessed to determine impairment.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody was previously assessed as impaired for Nutrients (TSI), however that parameter is no longer assessed to determine impairment per Rule 62-303, F.A.C.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody was previously impaired for Nutrients (TSI), however that parameter is no longer being assessed to determine impairment.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody was previously impaired for Nutrients (TSI), however that parameter is no longer being assessed to determine impairment.

This waterbody is impaired for this parameter based on failing bioassessments and nutrients have been determined to be the causative pollutant. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed using genetic marker and chemical tracer data. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List. This parameter is impaired for this waterbody based on the number of exceedances for the sample size and is being added to the 303(d) list. The water for WBID 1527B was assessed as WBID 1527 in cycle 1.

This waterbody is impaired for this parameter based on failing bioassessments and nutrients have been determined to be the causative pollutant. Data used in this assessment was provided by Pinellas County. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

This waterbody is impaired for this parameter based on failing linear vegetation surveys with a C of C < 2.5 and FLEPPC score > 25%. Data used in this assessment was provided by Pinellas County. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient threshold more than once in a three year period, and there is biological evidence indicating non attainment of the designated use. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

This waterbody is impaired for this parameter because the annual arithmetic means exceeded the applicable ENR criterion more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. Data that were available in FL STORET as Escherichia were manually added to the assessment because they were not available in the IWR Run 56 database.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size and is being added to the 303(d) list.

This parameter is impaired for this waterbody because the annual average chlorophyll-a values exceeded the IWR threshold for streams of 20 µg/L in 2010. Based on the median TN/TP ratio of 16, total nitrogen and total phosphorus are co-limiting nutrients. The period of record assessment, which uses all available data regardless of age, indicated potential impairment. However, data older than the verified period were excluded from the final assessment based on the availability of more recent data, and the final assessment was based on the recent data. Dissolved oxygen is impaired and historic chlorophyll-a has insufficient data. This parameter is being added to the 303(d) list. NITROGEN IS LIMITING NUTRIENT.

pp = 67 / 128; vp = 41 / 72. Verified impaired. Nutrient (total nitrogen) and BOD were identified as the causative pollutants based on Chl-a data/nutrient impairment. Verified period median TN = 1.13 mg/L (46 values), median TP = 0.23 mg/L (56 values), median BOD = 2.0 mg/L (42 values).

pp = No data; vp = 5 / 7. Verified impaired.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. There are insufficient data to determine the long-term geometric mean color and alkalinity yet the annual geometric mean chlorophyll-a exceeds the applicable criterion for a colored lake. This parameter is being added to the Verified List per 62-303.450(4) F.A.C. and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. There are insufficient data to determine the long-term geometric mean color and alkalinity yet the annual geometric mean chlorophyll-a exceeds the applicable criterion for a colored lake. This parameter is being added to the Verified List per 62-303.450(4) F.A.C. and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. There are insufficient data to determine the long-term geometric mean color and alkalinity yet the annual geometric mean chlorophyll-a exceeds the applicable criterion for a colored lake. This parameter is being added to the Verified List per 62-303.450(4) F.A.C. and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed based on land use. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This parameter is impaired for this waterbody based on the number of exceedances for a sample size less than 20. Fewer than twenty samples may be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a), F.A.C. This parameter is being added to the 303(d) list.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size. Median total nitrogen and total phosphorus values were not elevated relative to comparable waters and biochemical oxygen demand was identified as the causative pollutant because it was elevated relative to comparable waters (exceeded 2.0 mg/L). This parameter is being added to the 303(d) list.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size. Median total nitrogen and total phosphorus values were not elevated relative to comparable waters and biochemical oxygen demand was identified as the causative pollutant because it was elevated relative to comparable waters (exceeded 2.0 mg/L). This parameter is being added to the 303(d) list.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size and is being added to the 303(d) list.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

pp = Planning list; vp = Verified impaired. Annual average Chl-a values exceeded 20 µg/l in 2001 - 2006, and exceedance values were 57.77, 46.98, 10.27, 9.997, 29.37, 39.22, 21.81, 39.46 and 26.33 µg/L, respectively. Nitrogen is the limiting nutrient based on a median TN/TP ratio of 5.20 (96 values). Verified period median TN = 0.87 mg/l (96 values), median TP = 0.15 mg/l (99 values), and BOD median = 2.7 mg/l (95 values).

WBID name changed from Lake Parker to Lake Wire. This calculation has been done excluding the City of Lakeland data due to quality assurance issues.

This waterbody is impaired for this parameter because the annual geometric means exceeded the IWR threshold of 20 µg/L more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter based on failing bioassessments and nutrients have been determined to be the causative pollutant. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear, alkaline lake more than once in a three year period. This parameter will remain on the Verified List and the 303(d) List.

pp = No data; vp = 33 / 62 Verified impaired. Annual average Chl-a values exceeded 11 µg/l in all years from 1999-2004, and the values were 27.29, 32.09, 35.35, 15.15, and 24.51 µg/l, respectively. Nitrogen is the limiting nutrient based on a median TN/TP ratio of 7.9 (67 values). The verified period total nitrogen median = 1.65 mg/l (68 values), total phosphorus median = 0.22 mg/l (67 values), and the BOD median = 2.6 mg/l (47 values).

This waterbody is impaired for this parameter. The annual geometric mean exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody was previously impaired for Nutrients (TSI), however that parameter is no longer being assessed to determine impairment.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric mean exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

pp = No data; vp = Verified impaired. Annual average Chl-a values exceeded 11 µg/l in 2005, and the exceedance value was 25.99 µg/L. Nitrogen is the limiting nutrient based on a median TN/TP ratio of 5.56 (22 values). Verified period median TN = 1.11 mg/l (22 values), median TP = 0.24 mg/l (22 values), and BOD median = 3.15 mg/l (22 values). This waterbody is impaired for this parameter based on failing bioassessments and nutrients have been determined to be the causative pollutant. A stressor identification evaluation identified that best management practices would help to reduce stormwater runoff and lower anthropogenic sources of high conductivity. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. Pinellas County provided additional biological data used in this assessment.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Data that were available in FL STORET as Escherichia were manually added to the assessment because they were not available in the IWR Run 56 database. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period, and there is biological evidence indicating non-attainment of the designated use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed based on land use. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on failing linear vegetation surveys with an average C of C score < 2.5 and FLEPPC percent coverage of > 25%. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a) F.A.C. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody was previously impaired for Nutrients (TSI), however that parameter is no longer being assessed to determine impairment. This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody was previously impaired for Nutrients (TSI), however that parameter is no longer being assessed to determine impairment.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody was previously impaired for Nutrients (TSI), however that parameter is no longer being assessed to determine impairment.

This waterbody is impaired for this parameter based on failing bioassessments and nutrients have been determined to be the causative pollutant. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

PP - Potentially impaired; VP - Verified Impaired. PP - 3 chl-a means exceed threshold of 20 µg/L in 1993, 1996, and 1998. VP - 2 chl-a means exceed the threshold in 1998 and 2003. Nitrogen limited based on a TN/TP ratio of 1.76 (104 values) PP and 3.25 (61 values) VP. 61 TN values, median 1.744 mg/L. 63 TP values, median 0.72 mg/L.

This waterbody is impaired for this parameter based on failing bioassessments and nutrients have been determined to be the causative pollutant. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody was previously assessed as impaired for Nutrients (TSI), however that parameter is no longer assessed to determine impairment per Rule 62-303, F.A.C.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody was previously impaired for Nutrients (TSI), however that parameter is no longer being assessed to determine impairment. This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody was previously impaired for Nutrients (TSI), however that parameter is no longer being assessed to determine impairment.

This waterbody is impaired for this parameter based on failing bioassessments and nutrients have been determined to be the causative pollutant. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody was previously assessed as impaired for Nutrients (TSI), however that parameter is no longer assessed to determine impairment per Rule 62-303, F.A.C.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody was previously impaired for Nutrients (TSI), however that parameter is no longer being assessed to determine impairment. Through correspondence with Polk County, it was determined that station 21FLPOLKBANANA5 is not representative of the waterbody as a whole. Furthermore, the TN and TP samples collected at station 21FLPOLKBANANA4 on 10/19/2010 were determined to have been collected at station 21FLPOLKBANANA5. As per 62- 303.320(8) F.A.C., TN and TP samples collected at 21FLPOLKBANANA5 will be excluded from the assessment of WBID 1549B1 Lake Stahl, and the TN and TP AGM’s for the years of 2003, 2004, 2008 and 2010 have been recalculated omitting the non-representative results. This exclusion did not change the assessment status of TN or TP for Cycle 3.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody was previously impaired for Nutrients (TSI), however that parameter is no longer being assessed to determine impairment. Through correspondence with Polk County, it was determined that station 21FLPOLKBANANA5 is not representative of the waterbody as a whole. Furthermore, the TN and TP samples collected at station 21FLPOLKBANANA4 on 10/19/2010 were determined to have been collected at station 21FLPOLKBANANA5. As per 62- 303.320(8) F.A.C., TN and TP samples collected at 21FLPOLKBANANA5 will be excluded from the assessment of WBID 1549B1 Lake Stahl, and the TN and TP AGM’s for the years of 2003, 2004, 2008 and 2010 have been recalculated omitting the non-representative results. This exclusion did not change the assessment status of TN or TP for Cycle 3.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric mean exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

pp = 64 / 221; vp = 42 / 82 Verified impaired. Nutrients were identified as a causative pollutant based on Chl-a data/nutrient impairment verification.

pp = Potentially impaired; vp = Verified impaired. Annual average Chl-a values exceeded 11 µg/l in 1999 - 2005, and values were 13.91, 31.74, 12.85, 23.44, 3.363, 11.26 and 5.108 µg/l, respectively. Nitrogen is the limiting nutrient based on a median TN/TP ratio of 6.89 (69 values). The verified period total nitrogen median = 1.05 mg/l (69 values), total phosphorus median = 0.15 mg/l (77 values), and the BOD median = 3 mg/l (47 values).

Listed due to downgrade in shellfish harvesting classification.

Listed due to downgrade in shellfish harvesting classification.

This waterbody is impaired for this parameter because there were 21 days or more of beach advisories in the verified period. This is a beach WBID, which are assessed solely on beach advisory information received from DOH.^ This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter because there were 21 days or more of beach advisories in the verified period. This is a beach WBID, which are assessed solely on beach advisory information received from DOH.^ This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter because there were 21 days or more of beach advisories in the verified period. This is a beach WBID, which are assessed solely on beach advisory information received from DOH.^ This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

Beach advisories posted for a total of 5 days in 2002, 7 days in 2003, and 41 days in 2004.

This parameter is impaired for this waterbody because there were 21 days, or more, of beach advisories in 2009 and 2011. This is a beach WBID, which are assessed solely on beach advisory information received from DOH.^ This parameter is being added to the 303(d) list.

Beach advisories posted for a total of 8 days in 2002, 35 days in 2003, 18 days in 2004, 14 days in 2005, and 5 days in 2007.

This waterbody is impaired for this parameter because there were 21 days or more of beach advisories in the verified period. This is a beach WBID, which are assessed solely on beach advisory information received from DOH.^ This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter because there were 21 days or more of beach advisories in the verified period. This is a beach WBID, which are assessed solely on beach advisory information received from DOH.^ This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter because there were 21 days or more of beach advisories in the verified period. This is a beach WBID, which are assessed solely on beach advisory information received from DOH.^ This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

pp = Planning list; vp = Verified impaired. Annual average Chl-a values exceeded 11 µg/l in 2001 and 2003 - 2005, and exceedance values were 12.91, 13.33, 15.69, and 14.17 µg/L, respectively. Nitrogen is the limiting nutrient based on a median TN/TP ratio of 4.46 (87 values). Verified period median TN = 0.77 mg/l (88 values), median TP = 0.18 mg/l (97 values), BOD median = 2.0 mg/l (22 values). This parameter is impaired because the shellfish harvesting classification is not fully approved by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture and Consumer Services. Other coliform assessments for this WBID indicated no impairment. This parameter is being added to the 303(d) list.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. There is a DEP Adopted Fecal Coliform TMDL for this waterbody. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size. It was delisted in cycle 1 but is currently impaired and will be included on the cycle 2 Verified List and on the 303(d) list. Impaired for DO Cat 5 with BOD as causative pollutant. 'pp = 6 / 10; vp = 24 / 45 Verified impaired. TN median = 1.2 mg/L, TP median = 0.2 mg/L, BOD median = 4 mg/L (n=6, run35)

pp = No Data; vp = 13 / 22

This waterbody is impaired for this parameter based on failing bioassessments and nutrients have been determined to be the causative pollutant. Data used in this assessment was provided by Pinellas County. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criterion more than once in a three year period, and there is biological evidence indicating non attainment of the designated use. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

pp = 1 / 1; vp = 11 / 28

This waterbody is impaired for this parameter based on failing linear vegetation surveys with a C of C < 2.5 and FLEPPC score > 25%. Data used in this assessment was provided by Pinellas County. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List. This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed based on land use. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed using genetic marker and chemical tracer data. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62-303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. There is a DEP Adopted Fecal Coliform TMDL for this waterbody. The department is requesting EPA add this parameter to the 303(d) List.

This waterbody is impaired for this parameter based on failing bioassessments and nutrients have been determined to be the causative pollutant. A stressor identification evaluation identified that multiple water quality and hydrologic stressors contribute to the impairment. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. Pinellas County provided additional biological data used in this assessment.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. There is a DEP Adopted Fecal Coliform TMDL. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. Data that were available in FL STORET as Escherichia were manually added to the assessment because they were not available in the IWR Run 56 database. Station 21FLPDEM12- 02 was excluded in this assessment because the station was reassigned to WBID 1569 based on updated coordinates.

This waterbody is impaired for this parameter based on failing linear vegetation surveys with a C of C score < 2.5 and FLEPPC percent coverage of > 25%. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. Pinellas County provided additional biological data used in this assessment.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period, and there is biological evidence indicating non-attainment of the designated use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on failing bioassessments and nutrients have been determined to be the causative pollutant. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. Pinellas County provided additional biological data used in this assessment.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear alkaline lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on failing bioassessments and nutrients have been determined to be the causative pollutant. A stressor identification evaluation identified that multiple water quality and hydrologic stressors contribute to the impairment. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. Pinellas County provided additional biological data used in this assessment.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and nutrients have been identified as the causative pollutant. Samples used in this analysis were assessed against a time of day adjustment as described in 62-303.420(9), F.A.C. This parameter is being added to the Verified List and will remain on the 303(d) List. This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period, and there is biological evidence indicating non-attainment of the designated use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

pp = 2 / 6; vp = 17 / 24. Verified impaired. Nutrients (total phosphorus) were identified as the causative pollutant based on Chl-a data/nutrient impairment. Verified period median TN = 1.24 mg/L (19 values), median TP = 0.3 (18 values), median BOD = 1.8 (12 values).

This parameter is impaired for this waterbody based on the number of exceedances for the sample size and is being added to the 303(d) list.

This waterbody is impaired for this parameter based on failing bioassessments and nutrients have been determined to be the causative pollutant. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. USF Water Institute provided additional biological data used in this assessment.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a high color lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a high color lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on failing bioassessments and nutrients have been determined to be the causative pollutant. This parameter is being added to the Verified List and will remain on the 303(d) List. USF Water Institute provided additional biological data used in this assessment. This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period, and there is biological evidence indicating non-attainment of the designated use. This parameter is being added to the Verified List and will remain on the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period, and there is biological evidence indicating non-attainment of the designated use. This parameter is being added to the Verified List and will remain on the 303(d) List.

pp = No data; vp = Verified impaired. Annual average Chl-a values exceeded 20 µg/l in 2005, and the exceedance value was 54.42 µg/L. Nitrogen and phosphorus are limiting nutrients based on a median TN/TP ratio of 12.75 (22 values). Verified period median TN= 1.81 mg/l (22 values), median TP = 0.13 mg/l (22 values), and BOD median = 3.25 mg/l (22 values).

This waterbody is potentially impaired for this parameter based on data in the planning period. The previous impairment in the retired WBID 1584A is being carried over to WBID 1584A1; however, fecal coliform is no longer the applicable bacteria parameter for this waterbody classification. Enterococci will be included in the Strategic Monitoring Plan for this waterbody in order to collect the new applicable bacteria parameter. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody was previously assessed as impaired for Nutrients (TSI), however that parameter is no longer assessed to determine impairment per Rule 62-303, F.A.C.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed based on land use. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the nutrient threshold more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient threshold more than once in a three year period, and there is biological evidence indicating non-attainment of the designated use. This parameter is being added to the Verified List and will remain on the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size and is being added to the 303(d) list.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size and is being added to the 303(d) list.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

NITROGEN IS LIMITING NUTRIENT.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and nutrients have been identified as the causative pollutant. This parameter is being added to the Verified List and the department is requesting it remain on the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. There is a DEP Adopted Fecal Coliform TMDL for this waterbody. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on failing bioassessments and nutrients have been determined to be the causative pollutant. A stressor identification evaluation identified extensive anthropogenic development and extreme flow events contribute to the impairment. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. Pinellas County provided additional biological data used in this assessment. This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on failing linear vegetation surveys with an average C of C score < 2.5 and FLEPPC percent coverage of > 25%. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. Pinellas County provided additional biological data used in this assessment.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period, and there is biological evidence indicating non-attainment of the designated use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Data that were available in FL STORET as Escherichia were manually added to the assessment because they were not available in the IWR Run 56 database. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on failing linear vegetation surveys with an average C of C score < 2.5 and FLEPPC percent coverage of > 25%. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. USF Water Institute provided additional biological data used in this assessment.

pp = 6 / 15; vp = 11 / 24. Verified impaired.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size and is being added to the 303(d) list.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size and is being added to the 303(d) list. This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a) F.A.C. This parameter is being added to the 303(d) List.

pp = 12 / 45; vp = 12 / 34

Annual average Chl-a values exceeded 20 µg/l in 2005 and exceedance values were 66.97 µg/L. Nitrogen is the limiting nutrient based on a median TN/TP ratio of 3.45 (30 values). Verified period median TN = 1.85 mg/L (n = 32), median TP = 0.57 mg/L (n = 30), and BOD median = No data.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric mean exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

pp = 34 / 36; vp = 21 / 24

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size and is being added to the 303(d) list.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size and is being added to the 303(d) list.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the annual geometric means exceeding the criterion more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

Impaired based on the number of exceedances. This waterbody is impaired for this parameter based on failing linear vegetation survey results. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on failing rapid periphyton survey results. There are at least two temporally independent samples greater than 25% and this parameter is being added to the Verified List.

This waterbody is impaired for this parameter based on failing linear vegetation survey results. This parameter is being added to the 303(d) List.

PP - 32 / 117 Potentially impaired; VP - 39 / 119 Verified impaired. Nutrients were identified as a causative pollutant based on chlorophyll data/nutrient impairment verification (verified period total phosphorus median = 0.473 mg/l). (verified period total Nitrogen median = 2.565 mg/L). 4 BOD values (median = 6.5 mg/L) Co-limited by nitrogen and phosphorus.

PP - Potentially impaired; VP - Verified Impaired. VP - Annual average chl(a) values exceeded 20 µg/L in 1997-2003. Nitrogen is the limiting nutrient based on a TN/TP ratio median of 7.22. 130 TN values, median 2.4 mg/L. 133 TP values, median 0.401 mg/L.

Impaired based on the number of exceedances.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient threshold more than once in a three year period, and there is floral evidence indicating non attainment of designated use. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody was previously assessed as impaired for Nutrients (TSI), however that parameter is no longer assessed to determine impairment per Rule 62-303, F.A.C.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody was previously impaired for Nutrients (TSI), however that parameter is no longer being assessed to determine impairment. This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody was previously impaired for Nutrients (TSI), however that parameter is no longer being assessed to determine impairment.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody was previously assessed as impaired for Nutrients (TSI), however that parameter is no longer assessed to determine impairment per Rule 62-303, F.A.C.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody was previously impaired for Nutrients (TSI), however that parameter is no longer being assessed to determine impairment.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody was previously impaired for Nutrients (TSI), however that parameter is no longer being assessed to determine impairment.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. There is a DEP Adopted Fecal Coliform TMDL for this waterbody. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

Impaired with total nitrogen and biochemical oxygen demand identified as the causative pollutants.

Impaired based on the number of exceedances.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This parameter is impaired for this waterbody based on the number of exceedances for a sample size less than 20. Fewer than twenty samples may be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a), F.A.C. This parameter is being added to the 303(d) list.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

pp = 68/133; vp = 48 / 151 Verified Impaired. This listing may be removed because the Department has not been able to determine a causative pollutant for DO. Note that the WBID is not impaired for Chl-a. The verified period total nitrogen median = 1.095 mg/l (120 values), total phosphorus median = 0.07 mg/l (124 values), and BOD median = 2 mg/l (66 values).

This waterbody is impaired for this parameter based on the annual geometric means exceeding the criterion more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

pp = 75 / 398; vp = 73 / 315 Verified Impaired. Nutrients were identified as a causative pollutant based on Chl-a data/nutrient impairment verification.

pp = Potentially impaired; vp = Verified impaired. Annual average Chl-a values exceeded 11 µg/l in 1999 and 2001 - 2005, and values were 17.75, 14.84, 12.34, 18.95, 14.17 and 17.38 µg/l, respectively. Nitrogen is the limiting nutrient based on a median TN/TP ratio of 6.98 (150 values). Verified period total nitrogen median = 1.11 mg/l (152 values), total phosphorus median = 0.16 mg/l (159 values), and BOD = 2 mg/l (123 values).

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed based on land use. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. pp = 12 / 13; vp = 12 / 13

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed based on land use. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed using genetic marker and chemical tracer data. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62-303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed based on land use. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed using genetic marker and chemical tracer data. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed based on land use. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

pp = 69 / 76; vp = 14 / 18. Verified impaired. BOD was identified as the causative pollutant. Verified period median TN = 1.15 mg/L (13 values), median TP = 0.17 mg/L (17 values), median BOD = 2.0 mg/L (11 values).

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62-303.390(2)(f) F.A.C. There is a DEP Adopted Fecal Coliform TMDL for this waterbody. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed. There is a DEP Adopted Fecal Coliform TMDL for this waterbody. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed based on land use. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

pp = 25 / 36; vp = 21 / 28.

This waterbody is impaired for this parameter based on failing linear vegetation surveys with a C of C < 2.5 and FLEPPC score > 25%. Data used in this assessment was provided by Pinellas County. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List. pp = 6 / 13; vp = 2 / 12; Sufficient PP/VP data to assess. Exceedance rate for combined PP+VP (8/25) triggers VL. Rate for most recent 20 samples (4/20) does not. However, POR includes multiple exceedances in late 2006. Area is highly developed. Assessment based on Period of Record data.

pp = 45 / 197; vp = 33 / 122 Verified Impaired. Nutrients and BOD were identified as a causative pollutant based on Chl-a data/nutrient impairment verification.

pp = Potentially impaired; vp = Verified impaired. Annual average Chl-a values exceeded 11 µg/l in 1999 - 2002 and 2004, and values were 40.48, 26.65, 21.1, 23.06, and 23.87 µg/l, respectively. For the historical listing, annual average Chl-a) values in the verified period exceeded the minimum historical annual average value of 16.31 µg/l for 1990 -1994 by more than 50% in two consecutive years in 1999 (40.48 µg/L) and 2000 (26.65 µg/l). Nitrogen is the limiting nutrient based on a median TN/TP ratio of 6 (62 values). The verified period total nitrogen median = 1.14 mg/l (63 values), total phosphorus median = 0.18 mg/l (66 values), and BOD median = 3.05 mg/l (52 BOD values).

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a) F.A.C. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed based on land use. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed based on land use. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This parameter is impaired for this waterbody based on the number of exceedances for the sample size. Biochemical oxygen demand, total nitrogen, and total phosphorus were identified as the causative pollutants because they were elevated relative to comparable waters (exceeded 2.1 mg/L for BOD, 1.0 mg/L for TN, and 0.19 mg/L for TP). The period of record assessment, which uses all available data regardless of age, indicated potential impairment. However, data older than the verified period were excluded from the final assessment based on the availability of more recent data, and the final assessment was based on the recent data. This parameter is being added to the 303(d) list.

This parameter is impaired for this waterbody because the annual average chlorophyll-a values exceeded the alternative chlorophyll threshold of 15 µg/L in 2006, 2008, and 2011. Based on the median TN/TP ratio of 3.3, total nitrogen is the limiting nutrient. The period of record assessment, which uses all available data regardless of age, indicated potential impairment. However, data older than the verified period were excluded from the final assessment based on the availability of more recent data, and the final assessment was based on the recent data. Dissolved oxygen is impaired and historic chlorophyll-a has insufficient data. This parameter is being added to the 303(d) list.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on failing bioassessments and nutrients have been determined to be the causative pollutant. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a) F.A.C. This parameter is being added to the 303(d) List. This parameter is impaired for this waterbody based on the number of exceedances for the sample size. Biochemical oxygen demand and total phosphorus were identified as the causative pollutants because they were elevated relative to comparable waters (exceeded 2.1 mg/L for BOD and 0.19 mg/L for TP). The period of record assessment, which uses all available data regardless of age, indicated potential impairment. However, data older than the verified period were excluded from the final assessment based on the availability of more recent data, and the final assessment was based on the recent data. This parameter is being added to the 303(d) list.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Station 21FLCOSP32-03 (Smack's Bayou, 40th Avenue Northeast) had a median value that exceeded the 14 counts/100 mL criterion with at least 20 samples in the verified period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed based on land use. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This parameter is being added to the 303(d) List.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size and is being added to the 303(d) list.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in a three year period during the verified period. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62-303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using chemical tracer data and land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Station 21FLCOSP44-02 (Coffee Pot Bayou, Tidal) had a median value that exceeded the 14 counts/100 mL criterion with at least 20 samples in the verified period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on failing bioassessments and nutrients have been determined to be the causative pollutant. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear alkaline lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear alkaline lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

pp = 102 / 346; vp = 58 / 171 Verified impaired. There are a sufficient number of DO violations to place DO on the verified list. However, unable to link low DO to a causative pollutant (BOD or nutrients).

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

pp = 60 / 74; vp = 30 / 45. Verified impaired. Nutrients (total nitrogen and total phosphorus) and BOD were identified as the causative pollutants based on Chl-a data/nutrient impairment. Verified period median TN = 1.23 mg/L (41 values), median TP = 0.4 mg/L (42 values), median BOD = 2.5 mg/L (37 values). pp = Planning list; vp = Verified impaired. Annual average Chl-a values exceeded 11 µg/l in 2000 - 2001 and 2006, and exceedance values were 16.48, 13.81, and 23.13 µg/l, respectively. Nitrogen is the limiting nutrient based on a median TN/TP ratio of 3.21 (41 values). Verified period median TN = 1.23 mg/l (41 values), median TP = 0.4 mg/l (42 values), median BOD = 2.5 mg/l (37 values). This waterbody is impaired for this parameter based on the number of exceedances for the sample size This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. Additional data that were not available in the IWR Run 56 database but have been loaded into WIN were included in the assessment. This waterbody was incorrectly assessed as a marine (class 3M) waterbody but it is actually freshwater (class 3F). The class is being updated in the Impaired Waters Rule (IWR) database.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period, and there is biological evidence indicating non-attainment of the designated use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody was incorrectly assessed as a marine (class 3M) waterbody but it is actually freshwater (class 3F). The class is being updated in the Impaired Waters Rule (IWR) database.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. The data for this parameter was associated with retired WBID 1716C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. There is a DEP Adopted - EPA Approved Fecal Coliform TMDL for this waterbody and therefore, the Priority for TMDL Development is Low.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed based on land use. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This parameter is being added to the 303(d) List.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size and is being added to the 303(d) list.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed based on land use. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size and is being added to the 303(d) list.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a) F.A.C. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List. This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed based on land use. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

pp = 87 / 470; vp = 84 / 462

This waterbody is impaired for this parameter based on failing linear vegetation survey results. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on failing linear vegetation survey results. This parameter is being added to the 303(d) List.

This WBID is impaired for fecal coliforms based on the number of exceedances.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

Impaired based on the number of exceedances.

This waterbody is impaired for this parameter based on failing linear vegetation survey results. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient threshold more than once in a three year period, and there is floral data indicating non attainment of designated use. This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a) F.A.C. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

Impaired based on the number of exceedances.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Station 21FLHILL136 (Cockroach Bay at HCC Study Center) had a median value that exceeded the 14 counts/100 mL criterion with at least 20 samples in the verified period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed based on land use. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size and is being added to the 303(d) list.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed using genetic marker and chemical tracer data. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62-303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed based on land use. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.390(2)(f) F.A.C. There is a DEP Adopted Fecal Coliform TMDL for this waterbody. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

Waterbody name needs to be changed to Curiosity Creek.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This parameter is impaired for this waterbody because the shellfish harvesting classification is not fully approved by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture and Consumer Services. This parameter is being added to the 303(d) list.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

PP - 28/120 Potentially impaired; VP - 37/187 Verified impaired. For the 1998 303(d) analysis, the station data were incorrectly assigned to WBID 1840.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List.

PP - 23/33 Potentially impaired; VP - 28/59 Verified impaired

pp = 2 / 4; vp = 10 / 23. Verified impaired.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This parameter is impaired for this waterbody based on the number of exceedances for a sample size less than 20. Fewer than twenty samples may be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a), F.A.C. This parameter is being added to the 303(d) list. This parameter was previously verified impaired in cycle 2 under WBID 1825, which was subsequently revised into two WBIDs, a freshwater WBID 1825A and estuarine WBID 1825B. This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed using genetic marker and chemical tracer data. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62-303.390(2)(f) F.A.C. There is a DEP Adopted Fecal Coliform TMDL for this waterbody. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

Impaired based on the number of exceedances.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter because the annual arithmetic means exceeded the criteria more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and nutrients have been identified as the causative pollutant. Dissolved oxygen measurements taken within tidal areas are assessed using associated specific conductivity data (4,580 µmhos/cm, or 1,500 mg/L chloride, or 2.7 PSU salinity) for the determination of applicable freshwater or marine criteria as described in 62-303.320(11), F.A.C. Samples used in this assessment when the freshwater criteria apply were evaluated against a time of day adjustment as described in 62-303.420(9), F.A.C. This parameter is being added to the Verified List and it will remain on the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed using genetic marker and chemical tracer data. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62-303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the nutrient threshold of 11 µg/L more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed using genetic marker and chemical tracer data. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62-303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on two or more failing rapid periphyton surveys with >25% coverage periphyton. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This WBID is impaired for fecal coliforms based on the number of exceedances. This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Based on further analysis by DEP to investigate whether or not the impairment is due to natural conditions, anthropogenic sources could not be ruled out as the cause of the impairment and therefore this parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on failing bioassessments and nutrients has been determined to be the causative pollutant. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List.

PP - Insufficient data to calculate any annual mean Chl-a. VP - Impaired. 1 annual mean Chl-a exceeded the threshold in 2004. The annual mean Chl-a was 51.97 in 2004. 16 Chl-a values, range 1-510 µg/l, mean 57.1 µg/L. 76 TN values, Median 1.256 mg/L. 76 TP values, Median 0.05 mg/L. The community is phosphorus and nitrogen co-limited, but is more limited by phosphorus based on a Median TN/TP ratio of 23.1 from 76 TN/TP ratios.

This waterbody is impaired for this parameter based on failing linear vegetation survey results. This parameter is being added to the 303(d) List.

This waterbody is verified as impaired for nutrients because annual average chlorophyll-a values exceeded the listing threshold of 20 µg/L in 2009. TN and TP are co-limiting based on a median TN/TP ratio of 15.661 (n=25). This waterbody is impaired for this parameter based on failing linear vegetation survey results. This parameter is being added to the 303(d) List. Data from outside the verified period was used to support this assessment.

PP = 7 / 36; VP = 5 / 24

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a) F.A.C. This parameter is being added to the 303(d) List.

Impaired based on the number of exceedances. There are 16 additional samples collected at stations 21FLTPA 25020256 and 21FLTPA 27283758145059 after 6/30/09, with six samples exceeding 400 cfu/100 ml.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed using genetic marker and chemical tracer data. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List. This WBID was created from the retired WBID 1872 that was on the Verified List for this parameter.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

PP = 34 / 143; VP = 32 / 161

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on failing linear vegetation survey results. This parameter is being added to the 303(d) List.

Impaired based on the number of exceedances. Exceeds Class II criteria for bacteria. PP = Not impaired; VP = Impaired. The waterbody segment exceeded the 21 day beach closures, advisories, or warnings in 2003 with 75 days as per IWR Rule 62-303.360(1)(c). PP = Not impaired; VP = Impaired. The waterbody segment exceeded the 21 day beach closures, advisories, or warnings in 2003 with 142 days as per IWR Rule 62-303.360(1)(c). This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

Impaired based on the number of exceedances.

PP = 16 / 49; VP = 20 / 68

PP - Potentially impaired; VP - Verified Impaired. VP - Annual average chl(a) values exceeded 20 µg/L in 1998, 1999, 2000, 2002. Nitrogen is the limiting nutrient based on a TN/TP ratio median of 5.79. 52 TN values, median 1.42 mg/L. 52 TP values, median 0.269 mg/L.

This waterbody is verified as impaired based on the number of exceedances. Fewer than twenty samples may be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a).

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed using genetic marker and chemical tracer data. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62-303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on failing linear vegetation surveys with an average C of C score < 2.5 and FLEPPC percent coverage of > 25%. The department is evaluating if this waterbody meets the definition of a stream and is looking for more information on the hydrologic function of this waterbody. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

PP - 1/1 Insufficient data; VP - 11/21. Verified impaired.

PP - 34/67 Potentially impaired; VP - 38/77 Verified impaired

Impaired with biochemical oxygen demand identified as the causative pollutant. Data used to place water on 1998 303(d) list are from WBID 1968B. Previously known as "DIRECT RUNOFF TO BAY (Buttonwood Harbor/Sarasota Bay)" on the original 1998 303(d) list.

This waterbody is impaired for this parameter based on failing linear vegetation survey results. This parameter is being added to the 303(d) List.

Impaired with total nitrogen, total phosphorus and biochemical oxygen demand identified as the causative pollutants.

Impaired based on the number of exceedances.

PP - 37/118 Potentially impaired; VP - 40/135 Verified impaired. This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a) F.A.C. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

Impaired with total nitrogen, total phosphorus and biochemical oxygen demand identified as the causative pollutants.

Impaired based on the number of exceedances.

This waterbody is impaired because annual average Chl-a values exceeded 11 µg/l in 2008. Nitrogen is the limiting nutrient based on the TN/TP ratio median of 4.11 mg/L (n=14).

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

PP = 35 / 78; VP = 42 / 88 Verified Impaired

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This parameter is being added to the 303(d) List. This waterbody is verified as impaired based on the number of exceedances. Fewer than twenty samples may be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a).

This waterbody is verified as impaired for dissolved oxygen based on the number of exceedances. Total nitrogen and total phosphorus have been identified as the causative pollutants.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a) F.A.C. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List).

This waterbody is impaired for this parameter based on failing linear vegetation survey results. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

Impaired with biochemical oxygen demand identified as the causative pollutant.

Impaired based on the number of exceedances.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

PP = 5 / 14; VP = 6 / 29. EPA proposed TMDL in 2001.

This waterbody is impaired for this parameter based on failing linear vegetation survey results. This parameter is being added to the 303(d) List.

Impaired based on the number of exceedances.

Listed based on shellfish harvesting classification of prohibited by Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture. This waterbody is impaired for this parameter because the annual arithmetic means exceeded the criterion more than once in the most recent consecutive three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the IWR threshold of 11 µg/L more than once in a three year period. This parameter is being added to the 303(d) List.

Impaired based on the number of exceedances.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a) F.A.C. This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a) F.A.C. This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the 303(d) List. PP - 47 / 86 Potentially impaired; VP - 41 / 85 Verified impaired. Nutrients were identified as a causative pollutant based on chlorophyll data/nutrient impairment verification. Nitrogen limited.

This waterbody is impaired for this parameter based on failing rapid periphyton survey results. There are at least two temporally independent samples greater than 25% and this parameter is being added to the Verified List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody was previously impaired for Nutrients (TSI), however that parameter is no longer being assessed to determine impairment.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List. Listed based on change in shellfish harvesting classification (downgraded from approved to conditional).

This waterbody is impaired for this parameter because the annual arithmetic means exceeded the criterion more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter because the annual arithmetic means exceeded the criterion more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. The waterbody includes at least one sampling location (21FLCHARLBV002) that has a median fecal coliform MPN value that exceeds 14 counts per 100 ml for the verified period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

Annual average Chl a (µg/L) values exceeded 11 µg/L in 2001 (11.41) and 2005 (11.07). Nutrients are impaired with median values of [TN = 0.54 (230 observations), TP = 0.21 (230 observations), and BOD = 1.4 (219 observations)]. Waterbody is nitrogen limited based on the median TN/TP ratio of 2.14 (227 values).

This waterbody is impaired for this parameter because the annual arithmetic means exceeded the criterion more than once in a three year period. This parameter is being added to the 303(d) List.

Listed based on change in shellfish harvesting classification (downgraded from approved to conditional).

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

Impaired with total nitrogen, total phosphorus and biochemical oxygen demand identified as the causative pollutants.

Impairment for iron is due in part to naturally occurring groundwater inputs, however this WBID is included in a groundwater analysis report and the Department retained iron on the verified list because the Department could not eliminate possible anthropogenic sources. This waterbody is impaired because annual average Chl-a values exceeded 11 µg/l in 2008. Nitrogen is the limiting nutrient based on the TN/TP ratio median of 6.63 mg/L (n=18).

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List. This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

Listed based on shellfish harvesting classification of conditionally restricted by Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. The waterbody includes at least one sampling location that has a median fecal coliform MPN value that exceeds 14 counts per 100 ml for the verified period. This parameter is being added to the 303(d) List.

PP = 1 / 167; VP =9 / 45

Listed based on shellfish harvesting classification of conditionally restricted by Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. The waterbody includes at least one sampling location that has a median fecal coliform MPN value that exceeds 14 counts per 100 ml for the verified period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter because the annual arithmetic means exceeded the criterion more than once in the most recent consecutive three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. The waterbody includes at least one sampling location that has a median fecal coliform MPN value that exceeds 14 counts per 100 ml for the verified period. This parameter is being added to the 303(d) List. Impaired with total nitrogen identified as the causative pollutant. BOD assessed by dissolved oxygen parameter.

Impaired with total nitrogen identified as the causative pollutant.

Impaired based on the number of exceedances.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a) F.A.C. This parameter is being added to the 303(d) List.

Impaired based on the number of exceedances.

This waterbody is impaired for this parameter based on failing linear vegetation survey results. This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter based on failing linear vegetation survey results. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter because the annual arithmetic means exceeded the criterion more than once in a three year period. This parameter will be added to the 303(d) List.

This waterbody is impaired for this parameter because the annual arithmetic means exceeded the criterion more than once in a three year period. This parameter will be added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on failing linear vegetation survey results. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter because the annual arithmetic means exceeded the criterion more than once in the most recent consecutive three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a) F.A.C. This parameter is being added to the 303(d) List.

Impaired based on the number of exceedances.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on failing linear vegetation survey results. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter because the annual arithmetic means exceeded the criterion more than once in the most recent consecutive three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter because the annual arithmetic means exceeded the criterion more than once in the most recent consecutive three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed using genetic marker and chemical tracer data. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62-303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired because annual average Chl-a values exceeded 11 µg/l in 2008. Nitrogen and phosphorus are the limiting nutrients based on the TN/TP ratio median of 10.18 mg/L (n=42). Impaired with biochemical oxygen demand identified as the causative pollutant. This waterbody is impaired because annual average Chl-a values exceeded 11 µg/l in 2003 and 2008. Nitrogen is the limiting nutrient based on the TN/TP ratio median of 7.79 mg/L (n=20). This waterbody is impaired because annual average Chl-a values exceeded 11 µg/l in 2008. Nitrogen and phosphorus are the limiting nutrients based on a median TN/TP ratio of 20.19 (n=25) This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a) F.A.C. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

Impaired based on the number of exceedances.

Impairment for iron is due in part to naturally occurring groundwater inputs, however this WBID is included in a groundwater analysis report and the Department retained iron on the verified list because the Department could not eliminate possible anthropogenic sources.

PP - Potentially impaired; VP - Verified impaired. Annual average Chl-a values exceeded 20 µg/L in 1997, 1998. Nitrogen is the limiting nutrient based on a TN/TP ratio median of 4.92 (34 values) in the Planning Period and a TN/TP median of 5.50 (22 values) in the Verified Period.

Impaired based on the number of exceedances. Exceeds Class II criteria for bacteria. This waterbody is impaired for this parameter based on the number of exceedances for the sample size. The waterbody includes at least one sampling location that has a median fecal coliform MPN value that exceeds 14 counts per 100 ml for the verified period. This parameter is being added to the 303(d) List. Impairment for iron is due in part to naturally occurring groundwater inputs, however this WBID is included in a groundwater analysis report and the Department retained iron on the verified list because the Department could not eliminate possible anthropogenic sources. Impairment for iron is due in part to naturally occurring groundwater inputs, however this WBID is included in a groundwater analysis report and the Department retained iron on the verified list because the Department could not eliminate possible anthropogenic sources.

This waterbody is impaired for this parameter because the annual arithmetic means exceeded the criterion more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List. WBID 2056C, which was retired and split into WBIDs 2056C1 and 2056C2, was included in a groundwater analysis report during the Cycle 2 assessment, and the Department could not eliminate possible anthropogenic sources of iron. This waterbody is impaired for this parameter because the annual arithmetic means exceeded the criterion more than once in the most recent consecutive three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired because annual average Chl-a values exceeded 11 µg/l in 2006. Nitrogen is the limiting nutrient based on a median TN/TP ratio of 3.04 (n=94)

PP = No Data; VP = 9 / 24

This waterbody is listed as impaired for this parameter because the shellfish harvesting classification is not fully approved by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture and Consumer Services. This parameter is being added to the Verified List.

This waterbody is listed as impaired for this parameter because the shellfish harvesting classification is not fully approved by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture and Consumer Services. This parameter is being added to the Verified List.

PP = No Data; VP = Verified impaired. Annual average Chl-a values exceeded 11 µg/l in 2003 (19.46 µg/l). Nitrogen is the limiting nutrient based on a TN/TP ratio median of 1.34 mg/l (24 values). Impairment for iron is due in part to naturally occurring groundwater inputs, however this WBID is included in a groundwater analysis report and the Department retained iron on the verified list because the Department could not eliminate possible anthropogenic sources.

PP - 5/11; VP - 21/36

Annual average Chl a (µg/L) values exceeded 11 µg/L in 2003 (13.12) and 2006 (14.93). TN median = 0.729 mg/L (354 observations) and TP median = 0.185 mg/L (302 observations). Waterbody is nitrogen limited based on the median TN/TP ratio of 4.03 (276 values). No BOD observations.

This waterbody is listed as impaired for this parameter because the shellfish harvesting classification is not fully approved by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture and Consumer Services. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter because the annual arithmetic means exceeded the criteria more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter because the annual arithmetic means exceeded the criteria more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter because the annual arithmetic means exceeded the criterion more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter because the annual arithmetic means exceeded the criteria more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

Listed based on change in shellfish harvesting classification (downgraded from approved to conditional).

This waterbody is listed as impaired for this parameter because the shellfish harvesting classification is not fully approved by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture and Consumer Services. This parameter is being added to the 303(d) List.

Listed based on change in shellfish harvesting classification (downgraded from approved to conditional).

This waterbody is impaired for this parameter because the annual arithmetic means exceeded the criteria more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

Listed based on change in shellfish harvesting classification (downgraded from conditional to prohibited).

This waterbody is impaired for this parameter because the annual arithmetic means exceeded the criterion more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is listed as impaired for this parameter because the shellfish harvesting classification is not fully approved by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture and Consumer Services. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter because the annual arithmetic means exceeded the criteria more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter because the annual arithmetic means exceeded the criteria more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is listed as impaired for this parameter because the shellfish harvesting classification is not fully approved by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture and Consumer Services. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter because the long term average exceeded the criteria. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter because the long term average exceeded the criteria. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and nutrients have been identified as the causative pollutant. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. The waterbody includes at least one sampling location (21FLCHARGSV001 and 21FLCHARGSV005) that has a median fecal coliform MPN value that exceeds 14 counts per 100 ml for the verified period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

The shellfish harvesting classification of Prohibited, assigned to this WBID by the Shellfish Harvest Area Classification Program of the Florida Department of Agriculture and Consumer Services, is based on an administrative decision as a precautionary measure, and not water quality data. However, Fecal Coliform water quality data also indicate a bacteria problem in the current assessment period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the nutrient threshold of 11 µg/L more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. Listed based on change in shellfish harvesting classification (downgraded from conditional to prohibited).

This waterbody is impaired for this parameter because the annual arithmetic means exceeded the criteria more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and nutrients have been identified as the causative pollutant. Samples used in this assessment were evaluated against a time of day adjustment as described in 62-303.420(9), F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the nutrient threshold of 20 µg/L more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient threshold more than once in a three year period, and there is biological evidence indicating non-attainment of the designated use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient threshold more than once in a three year period, and there is biological evidence indicating non-attainment of the designated use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a) F.A.C. This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a) F.A.C. This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter based on the number of exceedances for the sample size This parameter is being added to the Verified List. This WBID is verified for impairment even though there are fewer than 20 samples because there are five or more temporally independent samples that do not meet the applicable water quality criterion (Rule 62-303.420(7)(a), FAC). This waterbody is impaired for this parameter based on the number of exceedances for the sample size This parameter is being added to the Verified List. VP - 15/22 Exceedances, VP Median = 4.25 mg/L, VP Average = 4.31 mg/L, VP MIN = 1.1 mg/L, VP MAX = 10. DATA FROM 2003, 2004. LINKED TO NUTRIENTS - VP TN = 2.016 mg/L, VP TP = 1.2 mg/L. BOTH TN AND TP EXCEED THRESHOLDS. NO BOD DATA.

PP - 26/58 Potentially impaired; VP - 14/39 Verified

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed using genetic marker and chemical tracer data, and land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List. The freshwater area previously assessed in WBID 2189 is now assessed as part of WBID 2189A. This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List. This WBID was created from retired WBID 2191 which was on the 303(d) List for this parameter. This WBID is verified for impairment even though there are fewer than 20 samples because there are five or more temporally independent samples that do not meet the applicable water quality criterion (Rule 62-303.420(7)(a), FAC). This waterbody is impaired for this parameter because the long term annual arithmetic mean exceeded the criterion. This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed using genetic marker and chemical tracer data, and land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

PP - 16/32 Potentially impaired; VP - 29/69 Verified This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.420(7)(a) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

PP - 29/53 Potentially impaired; VP - 64/98 Verified

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

Excluded from period of record assessment, as it is Impaired according to more recent data. This waterbody is impaired for this parameter based on the number of exceedances for the sample size, and anthropogenic sources have been confirmed using genetic marker and chemical tracer data, and land use. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62-303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.420(7)(a) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a) F.A.C. This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a) F.A.C. This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a) F.A.C. This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List. This WBID was created from the retired WBID 2228 that was also in category 5 (Impaired) for this parameter.

This waterbody is impaired for this parameter. The long term annual arithmetic mean exceeded the nutrient criteria. This parameter is being added to the 303(d) List. This WBID was created from the retired WBID 2228 that was also in category 5 (Impaired) for this parameter.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

PP - 38/66 Potentially impaired; VP -18/42 Verified

PP - 23/29 Potentially impaired; VP - 30/42 Verified This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List. This WBID was created from retired WBID 2234 which was on the 303(d) List for this parameter. This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed using genetic marker and chemical tracer data, and land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

PP - 24/34 Potentially impaired; VP - 17/25 Verified

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed using genetic marker and chemical tracer data, and land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a) F.A.C. This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed using genetic marker and chemical tracer data, and land use. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62-303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

PP - 12/32 Not impaired; VP - 14/26 Verified

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

PP - 30/32 Potentially impaired; VP - 25/30 Verified This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

Excluded from period of record assessment, as it is Impaired according to more recent data.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed using genetic marker and chemical tracer data, and land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List. This WBID was created from the retired WBID 2265B that was in category 3c (Planning List) for this parameter.

This waterbody is impaired for this parameter because the long term average exceeded the criteria. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

PP - 27/60 Potentially impaired; VP - 16/42 Verified

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List. This WBID was created from 3F Stream WBID 2270 that is also in category 5 (Impaired) for this parameter.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and nutrients have been identified as the causative pollutant. Dissolved oxygen measurements taken within tidal areas are assessed using associated specific conductivity data (4,580 µmhos/cm, or 1,500 mg/L chloride, or 2.7 PSU salinity) for the determination of applicable freshwater or marine criteria as described in 62-303.320(11), F.A.C. Samples used in this assessment when the freshwater criteria apply were evaluated against a time of day adjustment as described in 62-303.420(9), F.A.C. This parameter is being added to the Verified List and will remain on the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the nutrient threshold more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List. This WBID was created from the retired WBID 2284 that is also in category 5 (Impaired) for this parameter. This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List. This WBID was created from the retired WBID 2284 that was in category 3c (Planning List) for this parameter. This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

Excluded from period of record assessment, as it is Impaired according to more recent data.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

Area(s) included in the WBID have been downgraded from the 1979 approved classification to prohibited in 1985

PP - 26/31 Potentially impaired; VP - 11/20 Verified

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List. This parameter does not meet the impairment thresholds for this waterbody based on current data but cannot be delisted because the exceedance rate exceeds delisting requirements. This parameter is being added to the 303(d) list.

This parameter is impaired for this waterbody because the annual average chlorophyll-a values exceeded the IWR threshold of 11 µg/L in 2010. Based on the median TN/TP ratio of 20.89, total nitrogen and total phosphorus are co- limiting nutrients. The period of record assessment, which uses all available data regardless of age, indicated potential impairment. However, data older than the verified period were excluded from the final assessment based on the availability of more recent data, and the final assessment was based on the recent data. This parameter is being added to the 303(d) list.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is listed as impaired because the shellfish harvesting classification is not fully approved by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture. This parameter is being added to the 303(d) list. This waterbody is impaired for this parameter based on the number of exceedances for the sample size.

This parameter was originally listed as verified impaired on the Cycle 1 Verified List, but was delisted by amendment on February 7, 2012, because the prohibited classification is due to administrative reasons. However, this waterbody also contains some shellfish harvesting areas that are not fully approved not due to administrative reasons by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture; therefore this parameter is being added to the 303(d) list.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

This parameter is listed as impaired because the shellfish harvesting classification is not fully approved by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture. This parameter is being added to the 303(d) list. This waterbody is impaired for this parameter because the annual arithmetic means exceeded the criterion more than once in a three year period. This waterbody was placed in category 5 in a previous cycle but was not added to the Verified List because the more stringent element of the nutrient assessment, Nutrients (Historic Chlorophyll-a), was impaired and that parameter was added. Nutrients (Historic Chlorophyll-a) is currently being delisted because it is no longer assessed to determine impairment. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed using genetic marker chemical tracer data, and land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

PP - 29/30 Potentially impaired; VP - 14/20 Verified

PP - 23/29 Potentially impaired; VP - 14/20 Verified

Excluded from period of record assessment, as it is Impaired according to more recent data. Excluded from period of record assessment, as it is Impaired according to more recent data. Excluded from period of record assessment, as it is Impaired according to more recent data. This parameter is listed as impaired because the shellfish harvesting classification is not fully approved by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture. This parameter is being added to the 303(d) List. This parameter is impaired for this waterbody based on the number of exceedances and is being added to the 303(d) list. PP - 83/116 Potentially impaired; VP - 38/61 Verified. Linked to elevated TP (mean = 0.28 mg/L) Excluded from period of record assessment, as it is Impaired according to more recent data.

PP - 5/38 Not impaired; VP - 11/60 Verified

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

PP - 3/11 Potentially impaired; VP - 8/21 Verified

Area(s) included in the WBID have been downgraded from the 1979 approved classification to prohibited in 1985 and conditionally restricted since 1995

Area(s) included in the WBID have been downgraded from the 1979 approved classification to prohibited in 1985 and conditionally restricted since 1995

PP - 13/51 VP - 14/52 Median of 14 colonies per 100 ml also exceeded

Excluded from period of record assessment, as it is Impaired according to more recent data. Area(s) within the WBID have been downgraded from the 1979 approved classification to prohibited in 1985 and from conditionally approved to conditionally restricted in 1996.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List. Excluded from period of record assessment, as it is Impaired according to more recent data. Area(s) within the WBID have been downgraded from the 1979 approved classification to prohibited in 1985 and from conditionally approved to conditionally restricted in 1996. Area(s) within the WBID have been downgraded from the 1979 approved classification to prohibited in 1985 and from conditionally approved to conditionally restricted in 1996.

PP - 27/143 VP - 16/78

PP - 0/0 VP - 5/22

Area(s) within the WBID have been downgraded from the 1979 approved classification to conditionally restricted in 1996. Area(s) within the WBID have been downgraded from the 1979 approved classification to conditionally restricted in 1995. This parameter is listed as impaired because the shellfish harvesting classification is not fully approved by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture. This parameter will be added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and nutrients have been identified as the causative pollutant. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This parameter is listed as impaired because the shellfish harvesting classification is not fully approved by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture. This parameter is being added to the 303(d) list. Excluded from period of record assessment, as it is Impaired according to more recent data. Excluded from period of record assessment, as it is Impaired according to more recent data. Excluded from period of record assessment, as it is Impaired according to more recent data. Excluded from period of record assessment, as it is Impaired according to more recent data.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

This parameter is impaired for this waterbody based on the number of exceedances and is being added to the 303(d) list. Manually evaluated data. Excluded from period of record assessment, as it is Impaired according to more recent data.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in a three year period. This parameter is being added to the 303(d) List. No criteria in the Florida Water Quality Standards for BOD. Impaired based on DO criterion and TP is the causative pollutant. TP exceeded the IWR threshold of 0.22 mg/L. Excluded from period of record assessment, as it is Impaired according to more recent data.

This waterbody is impaired for this parameter based on failing bioassessments and nutrients have been determined to be the causative pollutant. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient threshold more than once in a three year period, and there is biological evidence indicating non-attainment of the designated use. This parameter is being added to the Verified List and will remain on the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. After further investigation, FDEP cannot rule out the possibility of anthropogenic sources. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This parameter is listed as impaired because the shellfish harvesting classification is not fully approved by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture.

No criteria in the Florida Water Quality Standards for BOD. impaired based on DO criterion and TN and TP are the causative pollutants. Excluded from period of record assessment, as it is Impaired according to more recent data.

Impaired based on DO criterion and TN and TP are the causative pollutants. TN exceeded the IWR threshold of 1.6 mg/L and TP exceeded the IWR threshold of 0.22 mg/L. Excluded from period of record assessment, as it is Impaired according to more recent data. Excluded from period of record assessment, as it is Impaired according to more recent data. Excluded from period of record assessment, as it is Impaired according to more recent data.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. After further investigation, FDEP cannot rule out the possibility of anthropogenic sources. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a) F.A.C. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on failing linear vegetation surveys with an average C of C score < 2.5 and FLEPPC percent coverage of > 25%. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient threshold more than once in a three year period, and there is biological evidence indicating non-attainment of the designated use. This parameter is being added to the Verified List and will remain on the 303(d) List.

PP - 10/37 Potentially impaired; VP - 15/56 Verified Linked to elevated TP levels in both the PP and VP (0.29 and 0.31 mg/l, respectively).

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This parameter is listed as impaired because the shellfish harvesting classification is not fully approved by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture.

This parameter is impaired for this waterbody based on the number of exceedances for a sample size less than 20. Fewer than twenty samples may be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a). This parameter is being added to the 303(d) list.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and nutrients have been identified as the causative pollutant. This parameter is being added to the Verified List and this parameter will remain on the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List. This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric mean exceeded the criterion more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and nutrients have been identified as the causative pollutant. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

PP - 22/38 Potentially impaired; VP - 34/59 Verified. Linked to elevated TP based on levels above the screening level during both the PP and VP (0.34 and 0.34 mg/l, respectively).

PP - 4/5 Potentially impaired; VP - 16/20 Verified

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a) F.A.C. This parameter is being added to the 303(d) List. PP - Chl-a potentially impaired; VP - Chl-a verified. Annual average Chl-a exceeded 20 µg/l in 1996, 1997, and 1999 - 2001. Phosphorus limiting based on median TN/TP ratios of 22 (152 values) during the PP and 21.3 (180 values) during the VP.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on failing rapid periphyton surveys with >25% coverage periphyton. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

This waterbody is impaired for this parameter based on failing linear vegetation surveys with a C of C < 2.5 and FLEPPC score > 25%. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a) F.A.C. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter will remain on the Verified List and the 303(d) List. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in a three year period. This parameter is being added to the 303(d) List.

No criteria in the Florida Water Quality Standards for BOD. Data exceed the DO criterion, and WBID is also impaired for nutrients based on chlorophyll; therefore, this WBID has been placed in category 5 even though no causative pollutant has been determined. The BOD median exceeded the threshold for streams; however, it was based on only 5 samples (10 are required). Excluded from period of record assessment, as it is Impaired according to more recent data.

This waterbody is impaired for this parameter based on failing linear vegetation surveys with an average C of C score < 2.5 and FLEPPC percent coverage of > 25%. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient threshold more than once in a three year period, and there is biological evidence indicating non-attainment of the designated use. This parameter is being added to the Verified List and will remain on the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient threshold more than once in a three year period, and there is biological evidence indicating non-attainment of the designated use. This parameter is being added to the Verified List and will remain on the 303(d) List.

Impaired based on DO criterion and TN and BOD are the causative pollutants. TN exceeded the IWR threshold of 1.6 mg/L and BOD exceeded the IWR threshold of 2.0 mg/L. 4B Cycle 1 assessment is equivalent to 4C Cycle 2 assessment. Excluded from period of record assessment, as it is Impaired according to more recent data. This is a blackwater stream. Excluded from period of record assessment, as it is Impaired according to more recent data. Excluded from period of record assessment, as it is Impaired according to more recent data. This parameter is impaired for this waterbody based on the number of exceedances for a sample size less than 20. Fewer than twenty samples may be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a). This parameter is being added to the 303(d) list. This parameter is impaired for this waterbody because the annual average chlorophyll-a values exceeded the IWR threshold of 11 µg/L in 2006. There were insufficient data from a single year to calculate the annual mean chlorophyll-a for that year; however, there were data available from four consecutive seasons using an adjacent year, so this data was used to calculate the annual mean chlorophyll-a per Rule 62-303.350(2)(e). Based on the median TN/TP ratio of 20, total nitrogen and total phosphorus are co- limiting nutrients. The period of record assessment, which uses all available data regardless of age, indicated potential impairment. However, data older than the verified period were excluded from the final assessment based on the availability of more recent data, and the final assessment was based on the recent data. This parameter is being added to the 303(d) list.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size, and anthropogenic sources have been confirmed using genetic marker and chemical tracer data. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62-303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

This waterbody is impaired for this parameter based on failing linear vegetation surveys with a C of C < 2.5 and FLEPPC score > 25%. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

This waterbody is impaired for this parameter based on failing linear vegetation surveys with a C of C < 2.5 and FLEPPC score > 25%. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List. This waterbody is impaired for this parameter based on the number of exceedances for the sample size, and anthropogenic sources have been confirmed using genetic marker and chemical tracer data. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

This parameter does not meet the impairment thresholds for this waterbody based on current data but cannot be delisted because the exceedance rate exceeds delisting requirements. The period of record assessment, which uses all available data regardless of age, indicated potential impairment. However, data older than the verified period were excluded from the final assessment based on the availability of more recent data, and the final assessment was based on the recent data. This parameter will remain on the 303(d) list.

PP - 10/13 VP - 12/45 DO met verification threshold of IWR, TN and BOD were identified as causative pollutants. PP median TN = 0.996 mg/L (n=8), median TP = 0.1925 mg/L (n=12), no BOD data. VP median TN = 1.295 mg/L (n=12), median TP = 0.1755 mg/L (n=16), median BOD = 2.5 mg/L (n=25).

Annual average for 2003 exceeds the 11 µg/L threshold for estuaries. Only annual average is from 2003 - 17.17 µg/L. Nitrogen identified as the limiting nutrient based on all the TN/TP ratios less than 10. This waterbody is impaired for this parameter based on the number of exceedances for the sample size and nutrients have been identified as the causative pollutant. Dissolved oxygen grab samples used in this analysis were assessed against a time of day adjustment as described in 62-303.420(9), F.A.C. This parameter is being added to the Verified List and will remain on the 303(d) List.

This waterbody is impaired for this parameter based on failing linear vegetation surveys with a C of C < 2.5 and FLEPPC score > 25%. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the nutrient threshold more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

pp = 16 / 73 Potentially Impaired; vp = 17 / 74, Impaired. Delisted from the Consent Decree List in the 1st cycle, assessment but re-listed in the 2nd assessment cycle. pp = 31 / 72, Potentially Impaired; vp = 38 / 83 Impaired This waterbody is impaired for this parameter based on the number of exceedances for the sample size, and anthropogenic sources have been confirmed using genetic marker and chemical tracer data. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62-303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on failing bioassessments and nutrients have been determined to be the causative pollutant. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a high color lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a high color lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a high color lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on failing bioassessments and nutrients have been determined to be the causative pollutant. A stressor identification evaluation identified elevated nutrients are causing SCI failures. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. Alachua County biological data were included in the assessment.

This waterbody is impaired for this parameter because the annual geometric means exceeded the nutrient threshold more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period, and there is biological evidence indicating non-attainment of the designated use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period, and there is biological evidence indicating non-attainment of the designated use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a high color lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size and is being added to the 303(d) list.

This parameter is impaired for this waterbody based on the number of exceedances for a sample size less than 20. Fewer than twenty samples may be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a), F.A.C. This parameter is being added to the 303(d) list. pp = 4 / 7 Potentially Impaired; vp = 10 / 20, Impaired. This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a high color lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size. Total nitrogen, total phosphorus, and BOD were identified as causative pollutants because they exceeded the TN, TP, and BOD thresholds for identification of a causative pollutant (TN exceeded 1.7 mg/L, TP exceeded 0.11 mg/L, and BOD exceeded 2.9 mg/L). The period of record assessment, which uses all available data regardless of age, indicated potential impairment. However, data older than the verified period were excluded from the final assessment based on the availability of more recent data, and the final assessment was based on the recent data. This parameter is being added to the 303(d) list.

This waterbody is impaired for this parameter based on failing bioassessments and nutrients have been determined to be the causative pollutant. A stressor identification evaluation identified elevated NO3+NO2 and extensive anthropogenic development and alteration of the watershed contribute to the impairment. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. Alachua County biological data were included in the assessment.

pp = 31 / 96, Potentially Impaired; vp = 40 / 84 Impaired

This parameter is impaired for this waterbody based on the number of exceedances for a sample size less than 20. Fewer than twenty samples may be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a), F.A.C. This parameter is being added to the 303(d) list. pp = 3 / 9, Potentially Impaired; vp = 5 / 18 Impaired pp = 8 / 26 Potentially Impaired; vp = 8 / 27 Impaired.

This waterbody is impaired for this parameter. The annual geometric means exceeded the criteria more than once in a three-year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

pp = 12 / 14 Potentially Impaired ; vp = 38 / 44 Impaired. DO met the verification threshold and TN was identified as the causative pollutant. 44 TN measurements, median 1.99 mg/L. 44 TP measurements, median 0.12 mg/L. No BOD measurements.

This waterbody is impaired for this parameter because the annual geometric means exceeded the nutrient threshold more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period, and there is biological evidence indicating non-attainment of the designated use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period, and there is biological evidence indicating non-attainment of the designated use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on failing linear vegetation surveys with an average C of C score < 2.5 and FLEPPC percent coverage of > 25%. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period, and there is biological evidence indicating non-attainment of the designated use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size. Total nitrogen and total phosphorus were identified as the causative pollutant because they exceeded the TN threshold of 1.54 mg/L and TP threshold of 0.12 mg/L for identification of a causative pollutant. The period of record assessment, which uses all available data regardless of age, indicated potential impairment. However, data older than the verified period were excluded from the final assessment based on the availability of more recent data, and the final assessment was based on the recent data. This parameter is being added to the 303(d) list.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size. Total nitrogen and total phosphorus were identified as the causative pollutant because they exceeded the TN threshold of 1.54 mg/L and TP threshold of 0.12 mg/L for identification of a causative pollutant. The period of record assessment, which uses all available data regardless of age, indicated potential impairment. However, data older than the verified period were excluded from the final assessment based on the availability of more recent data, and the final assessment was based on the recent data. This parameter is being added to the 303(d) list.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear acidic lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear acidic lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear acidic lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size. Total nitrogen was identified as a causative pollutant because it exceeded the TN threshold for identification of a causative pollutant of 1.54 mg/L. The period of record assessment, which uses all available data regardless of age, indicated potential impairment. However, data older than the verified period were excluded from the final assessment based on the availability of more recent data, and the final assessment was based on the recent data. This parameter is being added to the 303(d) list.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear alkaline lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on two or more failing rapid periphyton surveys with >25% coverage of periphyton. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the criteria more than once in a three-year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter. The annual geometric means exceeded the criteria more than once in a three-year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

DO met the listing threshold and the causative pollutant is total nitrogen. There are 12.27% urban and built up and 43.53% upland forest land uses.

pp = 23 / 29 Potentially Impaired; vp = 13 / 14 Impaired. DO met the verification threshold and TN was identified as the causative pollutant. 11 TN measurements, median 2.73 mg/L. 14 TP measurements, median 0.12 mg/L. 5 BOD measurements, median 1.0 mg/L. Fecal coliform data exceed the verification threshold; therefore, this WBID is being placed on the Cycle 2 Verified List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a) F.A.C. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on failing linear vegetation survey results. This parameter is being added to the 303(d) List.

Dissolved oxygen data exceed the verification threshold, and total nitrogen is the causative pollutant. This WBID was proposed for delisting from the 1998 303(d) List in Cycle 1. Silver data exceeded the verification threshold; further analysis confirmed this assessment. Therefore, this WBID is being placed on the Cycle 2 Verified List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

Fecal coliform data exceed the verification threshold; therefore, this WBID is being placed on the Cycle 2 Verified List.

This waterbody is impaired for this parameter based on failing linear vegetation survey results. This parameter is being added to the 303(d) List. The waterbody type for this WBID in IWR Run 52 is Class I (1); however, the classification will be revised to Class III Fresh (3F).

This waterbody is impaired for this parameter based on failing linear vegetation survey results. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient threshold more than once in a three year period, and there is floral evidence indicating nonattainment of designated use. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a high color lake more than once in a three year period. This parameter will be added to the Verified List and the 303(d) List.

Dissolved oxygen data exceed the verification threshold, and total nitrogen and biochemical oxygen demand are the causative pollutants.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List. This waterbody is impaired for this parameter based on failing linear vegetation survey results. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear, acidic lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear, acidic lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear, acidic lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on failing rapid periphyton survey results. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a high color lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a high color lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a high color lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter based on failing linear vegetation surveys with an average C of C score < 2.5 and FLEPPC percent coverage of > 25%. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. There is a Reasonable Assurance Plan (RAP) in development for Mosquito Lagoon.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. There is a Reasonable Assurance Plan (RAP) in development for Mosquito Lagoon.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. There is a Reasonable Assurance Plan (RAP) in development for Mosquito Lagoon.

This parameter is listed as impaired because the shellfish harvesting classification is not fully approved by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture. This parameter is being added to the 303(d) list.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. There is a Reasonable Assurance Plan (RAP) in development for Mosquito Lagoon.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. There is a Reasonable Assurance Plan (RAP) in development for Mosquito Lagoon. This waterbody is listed as impaired for this parameter because the shellfish harvesting classification is not fully approved by the Shellfish Harvest Area Classification Program of the department of Agriculture and Consumer Services. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. There is a Reasonable Assurance Plan (RAP) in development for Mosquito Lagoon.

DO met the verification threshold and total nitrogen was identified as the causative pollutant.

This parameter is impaired based on the number of exceedances for the sample size. Total nitrogen was identified as a causative pollutant because it was elevated relative to comparable reference condition waters (exceeded 1.0 mg/L). Total phosphorus and biochemical oxygen demand medians were both below their respective thresholds. Based on a TN/TP median of 25, total nitrogen and total phosphorus are co-limiting nutrients. This WBID drains directly to 2963F1 which is part of the Indian River Lagoon TMDL with listed load reductions of 35% and 47% for TN and TP respectively. The period of record assessment, which uses all available data regardless of age, indicated potential impairment. However, data older than the verified period were excluded from the final assessment based on the availability of more recent data, and the final assessment was based on the recent data.

This waterbody is impaired for this parameter because the annual geometric means exceeded the nutrient threshold at least twice in a consecutive three year period during the verified period. The most recent data indicates non- impairment, however, this parameter cannot be placed in category 2 (not impaired) because the delisting requirement of three consecutive years of (AGM / AAM / LTA) chlorophyll-a values below (criterion) has not been met. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

DO met the verification threshold and total nitrogen and BOD were identified as the causative pollutants. This waterbody is likely a blackwater stream.

This parameter is listed as impaired because the shellfish harvesting classification is not fully approved by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture. This parameter is being added to the 303(d) list. This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Station 21FLSEAS75SEAS050 (10 yards within Crane Creek) had a median value that exceeded the 14 counts/100 mL criterion with at least 20 samples in the verified period. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List. This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Station 21FLSEAS75SEAS010 (Mouth of Eau Gallie River) had a median value that exceeded the 14 counts/100 mL criterion with at least 20 samples in the verified period. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List. This waterbody is listed as impaired for this parameter because the shellfish harvesting classification is not fully approved by the Shellfish Harvest Area Classification Program of the department of Agriculture and Consumer Services. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

This parameter is listed as impaired because the shellfish harvesting classification is not fully approved by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture. This parameter is being added to the 303(d) list. This parameter is listed as impaired because the shellfish harvesting classification is not fully approved by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture. This parameter is being added to the 303(d) list. This parameter is listed as impaired because the shellfish harvesting classification is not fully approved by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture. This parameter is being added to the 303(d) list.

This waterbody is impaired for this parameter. The annual geometric mean exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

Fecal coliforms met verification thresholds.

Annual mean exceeded 20 µg/L in 2003, and the value was 33.5 µg/L. TN and TP are co-limiting nutrients based on a median TN/TP ratio of 13.12 (n=20). Additionally, nutrients were identified as the causative pollutant for dissolved oxygen impairment in Cycles 1 and 2.

Fecal coliforms met verification thresholds.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size, and anthropogenic sources have been confirmed using genetic marker and chemical tracer data. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62-303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

PP - 58/67 values below DO criterion. VP - 40/47 values below DO criterion. DO met verification threshold of IWR, and nitrogen and phosphorus are causative pollutants (TN median = 2.3 mg/L, TP median = 0.37 mg/L). 68 DO values, median 1.99 mg/L, mean 2.61 mg/L, range 8.55 - 0.29 mg/L.

Fecal coliforms met verification thresholds.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear, alkaline lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the criteria more than once in a three-year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the criteria more than once in a three-year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter based on the number of exceedances for the sample size, and anthropogenic sources have been confirmed using genetic marker and chemical tracer data. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62-303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size, and anthropogenic sources have been confirmed using genetic marker and chemical tracer data. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62-303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear, alkaline lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear, alkaline lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear, alkaline lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear, alkaline lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear, alkaline lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size, and anthropogenic sources have been confirmed using genetic marker and chemical tracer data. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62-303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

Fecal coliforms met verification thresholds.

This waterbody is impaired for this parameter based on failing linear vegetation surveys with an average C of C score < 2.5 and FLEPPC percent coverage of > 25%. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear, alkaline lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear, alkaline lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

Fecal coliforms met verification thresholds.

This waterbody is impaired for this parameter based on failing bioassessments and nutrients have been determined to be the causative pollutant. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear, acidic lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear, acidic lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear, acidic lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on failing linear vegetation surveys with an average C of C score < 2.5 and FLEPPC percent coverage of > 25%. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear, alkaline lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear, alkaline lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a high color lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a) F.A.C. This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter based on failing bioassessments and nutrients have been determined to be the causative pollutant. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear, alkaline lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear, alkaline lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear, alkaline lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear, alkaline lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on failing bioassessments and nutrients have been determined to be the causative pollutant. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear, alkaline lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear, alkaline lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear, alkaline lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired because the annual average for 2008 exceeded the threshold of 20 µg/ for streams. Nitrogen and phosphorus are co-limiting nutrients based on TN/TP ratios of 6.286 to 19.89 with a median of 12.051 (n = 21) over the verified period.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed using genetic marker and chemical tracer data. There is also a DEP Adopted Fecal Coliform TMDL. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

Fecal coliforms met verification thresholds.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

PP - 19/36 values exceed criterion. VP - 12/21 values exceed criterion. Coliform median 510 colonies/100ml, range 30 - 4,100 colonies/100ml. No more than 2 values per month.

PP - 18/32 values exceed criterion. VP - 11/20 values exceed criterion. Coliform median 440 colonies/100ml, range 8 - 3,100 colonies/100ml.

This parameter is impaired based on the number of exceedances (7) for a samples size less than 20. Fewer than twenty samples may be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a). This parameter is being added to the 303(d) list.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear, alkaline lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear, alkaline lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is listed as impaired for this parameter because the shellfish harvesting classification is not fully approved by the Shellfish Harvest Area Classification Program of the department of Agriculture and Consumer Services. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

This waterbody is impaired for this parameter based on failing linear vegetation surveys with an average C of C score < 2.5 and FLEPPC percent coverage of > 25%. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient threshold more than once in a three year period, and there is biological evidence indicating non-attainment of the designated use. This parameter is being added to the Verified List and will remain on the 303(d) List.

This waterbody is listed as impaired for this parameter because the shellfish harvesting classification is not fully approved by the Shellfish Harvest Area Classification Program of the department of Agriculture and Consumer Services. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

This waterbody is listed as impaired for this parameter because the shellfish harvesting classification is not fully approved by the Shellfish Harvest Area Classification Program of the department of Agriculture and Consumer Services. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

PP = 2 / 5 Insufficient Data; VP = 5 / 9 Impaired

This waterbody is impaired for this parameter based on failing linear vegetation surveys with a C of C < 2.5 and FLEPPC score > 25%. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This parameter is impaired based on the number of exceedances (5) for a samples size less than 20. Fewer than twenty samples may be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a). This parameter is being added to the 303(d) list. This waterbody is impaired for this parameter based on failing linear vegetation surveys with a C of C < 2.5 and FLEPPC score > 25%. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

Impaired based on number of exceedances.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This parameter is impaired based on the number of exceedances for the sample size and is being added to the 303(d) list.

This waterbody is impaired for this parameter based on failing linear vegetation survey results. This parameter is being added to the 303(d) List.

Dissolved oxygen data exceed the verification threshold, and total nitrogen and total phosphorus are the causative pollutants.

This waterbody is impaired for this parameter based on failing linear vegetation survey results. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient threshold more than once in a three year period, and there is floral evidence indicating nonattainment of designated use. This parameter is being added to the 303(d) List.

This parameter is impaired based on the number of exceedances (5) for a samples size less than 20. Fewer than twenty samples may be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a). This parameter is being added to the 303(d) list.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on failing linear vegetation survey results. This parameter is being added to the 303(d) List.

Dissolved oxygen data exceed the verification threshold, and total nitrogen, total phosphorus and biochemical oxygen demand are the causative pollutants.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List. This waterbody is impaired for this parameter. The annual geometric mean exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric mean exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric mean exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

PP = 0 / 1 Insufficient data; VP = 7 / 25, Impaired

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

This parameter is impaired based on the number of exceedances for the sample size and will be placed on the 303(d) list.

This WBID will remain on the 303(d) list in Cycle 2 and will be verified as impaired. This WBID was proposed for delisting from the 1998 303(d) List in Cycle 1.

PP = 1 / 3 Insufficient data; VP = 12 / 31, Impaired

Impaired by the IWR threshold and BOD was found to be the causative pollutant. BOD exceeded the threshold of 2.0 mg/L. TN/TP median = 7.04, standard deviation 5.24, range 1.67 - 28.65, observations 24. Placed on the 1998 303(d) list based on listing for WBID 3189. TMDL proposed by EPA 9-30- 06.

This waterbody is impaired for this parameter based on failing linear vegetation surveys with a C of C < 2.5 and FLEPPC score > 25%. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient threshold more than once in a three year period, and there is biological evidence indicating non attainment of the designated use. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List. PP - 75/126 Potentially Impaired, VP - 52/109 Verified Linked to nutrients, with both nitrogen and phosphorous as limiting nutrients, colimitation of Nitrogen and Phosphorus, TN during VP = 1.445 mg/L, TP during VP = 0.139 mg/L.

This waterbody is impaired for this parameter based on failing linear vegetation surveys with a C of C < 2.5 and FLEPPC score > 25%. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed using genetic marker and chemical tracer data. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This WBID is impaired for fecal coliforms based on the number of exceedances.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and will be added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This parameter is being added to the 303(d) List.

This waterbody is verified as impaired based on the number of exceedances. Fewer than twenty samples may be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a).

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on failing linear vegetation survey results. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI). However, Nutrients (TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (Historic TSI). However, Nutrients (Historic TSI) is being removed from the 303(d) List per Rule 62-303.720(2)(L), F.A.C., because it is no longer assessed to determine impairment. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This waterbody was previously listed as impaired on the Verified List for Nutrients (TSI) and Nutrients (Historic TSI). However, Nutrients (TSI) and Nutrients (Historic TSI) are being removed from the 303(d) List per Rule 62- 303.720(2)(L), F.A.C., because they are no longer assessed to determine impairment. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This parameter is being added to the 303(d) List.

This WBID is impaired for fecal coliforms based on the number of exceedances.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

PP = 7 / 49, Not impaired; VP = 7 / 39, Impaired. This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three-year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

PP = 7 / 8, Potentially impaired; VP = 20 / 23, Impaired.

This waterbody is impaired for this parameter based on failing linear vegetation survey results. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on failing linear vegetation survey results. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient threshold more than once in a three-year period, and there is floral evidence indicating nonattainment of designated use. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on failing linear vegetation survey results. This parameter is being added to the 303(d) List.

This WBID is impaired for fecal coliforms based on the number of exceedances.

This waterbody is verified as impaired for nutrients because annual average chlorophyll-a values exceeded the listing threshold of 20 µg/L in 2004 and 2007–2009. TN and TP are co-limiting based on a median TN/TP ratio of 18.392 (n=237).

This waterbody is verified as impaired for dissolved oxygen based on the number of exceedances. Biochemical oxygen demand has been identified as the causative pollutant. This waterbody is verified as impaired for nutrients because annual average chlorophyll-a values exceeded the listing threshold of 20 µg/L in 2004 and 2009. TN and TP are co-limiting based on a median TN/TP ratio of 10.553 (n=19). This waterbody is impaired for this parameter based on failing linear vegetation survey results. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient threshold more than once in a three-year period, and there is floral evidence indicating nonattainment of designated use. This parameter is being added to the 303(d) List. This waterbody is verified as impaired for dissolved oxygen based on the number of exceedances. Biochemical oxygen demand has been identified as the causative pollutant. This WBID is impaired for fecal coliforms based on the number of exceedances.

Listed based on downgrade of shellfish harvesting classification.

PP - Insufficient data to calculate any mean. VP - Impaired. 1 Chl-a annual mean exceeded the threshold. The annual mean Chl-a concentration was 26.78 µg/L. 12 TN values, Median 1.94 mg/L, 11 TP values, Median 0.23 mg/L. The community is nitrogen limited based on a Median TN/TP ratio of 7.9 calculated from 11 TN/TP ratios. This waterbody is verified as impaired for dissolved oxygen based on the number of exceedances. Total nitrogen and biochemical oxygen demand have been identified as the causative pollutants. This WBID is impaired for fecal coliforms based on the number of exceedances.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Based on further analysis by DEP to investigate whether or not the impairment is due to natural conditions, anthropogenic sources could not be ruled out as the cause of the impairment and therefore this parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient threshold more than once in a three-year period, and there is floral evidence indicating nonattainment of designated use. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

No Beach advisories in 2000, 2001, 2003, 2006 or 2007. 6 advisory days in 2002, 91 advisory days in 2004 and 223 in 2005.

PP - 3/3 Potentially Impaired; VP - 20/54 Verified

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

PP - 2/11 Not Impaired; VP - 25/58 Verified Potential sources may include agrochemicals, fungicides, algaecides, soil erosion, vehicle brake pads, roof runoff, etc based on the report "Land Use Changes and Water Quality Impacts: Copper Contamination in St. Lucie Estuary, Florida."

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This parameter is impaired because annual average chlorophyll-a values exceeded the 20 µg/L threshold in 2003, 2004 and 2009. Based on median TN/TP ratio of 21.25, TN and TP were identified as co-limiting nutrients.

This waterbody is impaired for this parameter based on failing linear vegetation survey results. This parameter is being added to the 303(d) List.

PP = 145 / 148; VP = 91 / 99 Impaired by the IWR threshold and nutrients were found to be the causative pollutant. TN (2.2 mg/L) exceeded the threshold of 1.6 mg/L. TP (0.75 mg/L) exceeded the threshold of 0.22 mg/L. TN/TP median = 2.8 standard deviation of 2.2, range of 1.26 - 12.2, observations 122. New listing from Cycle 2.

PP = 39 / 45; VP = 25 / 38 Impaired by the IWR threshold and nutrients were found to be the causative pollutant. TN (3.1 mg/L) exceeded the threshold of 1.6 mg/L. TP (1.2 mg/L) exceeded the threshold of 0.22. BOD (4.65 mg/L) exceeded the threshold of 2.0 mg/L and had 6 observations. TN/TP median = 2.3, standard deviation of 2.5, range 1.1 -12.1, observations 44. A TMDL has already been proposed by EPA, 9/30/2006.

The annual average Chl-a value exceeded the IWR threshold of 20 µg/L in 2006 (60.87 µg/L). TP (1.20 mg/L) exceeded the threshold of 0.22 mg/L. Data indicate that the WBID is nitrogen limited (TN/TP median = 2.34, standard deviation of 2.48, range 1.09 -12.13, observations 44). A TMDL has already been proposed by EPA, 9/30/2006.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size and is being added to the 303(d) list.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period, and there is biological evidence indicating non-attainment of the designated use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period, and there is biological evidence indicating non-attainment of the designated use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on failing linear vegetation survey results. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient threshold more than once in a three year period, and there is biological evidence indicating non attainment of designated use. This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter based on failing linear vegetation survey results. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient threshold more than once in a three year period, and there is biological evidence indicating non attainment of designated use. This parameter is being added to the 303(d) List.

PP=929/1171; VP=501/648 Impaired by the IWR threshold and nutrients were found to be the causative pollutant. TN (1.8 mg/L) exceeded the threshold of 1.6 mg/L. TP (0.35 mg/L) exceed the threshold of 0.22 mg/L. BOD (2.0 mg/L) did not exceed the threshold of 2.0 mg/L and had 22 observations. TN/TP median = 4.6, standard deviation 3.9, range 1.85 - 38.8, observations 356. A TMDL has been proposed by EPA, 9/30/2006.

PP=2/10; VP=7/29

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

PP=11/13; VP=32/51 Impaired by the IWR threshold and nutrients were found to be the causative pollutant. The annual average Chl-a value exceeded the threshold in 2006 (23.9 µg/L). BOD (2.0 mg/L) did not exceed the threshold of 2.0 mg/L and had 35 observations. TN/TP median = 68.8, standard deviation of 66.9, range 2.4 - 225.7, observations 122. New listing from Cycle 2.

The annual average Chl-a value exceeded the threshold of 20.0 µg/L in 2006 (23.92 µg/L). TN (0.67 mg/L) did not exceed the threshold of 1.6 mg/L. Data indicate that the WBID is phosphorous limited. TN/TP median = 68.75, standard deviation of 66.96, range 2.42 - 225.7, observations 122. New listing from Cycle 2. Nutrient concentrations are very low. Therefore, elevated chlorophyll may be due to standing water behind the flow-way to the lake.

PP - Not impaired; VP - Verified impaired. Annual Average Chl-a (µg/L) value exceeded 20 µg/L in 2004 (60.59). 377 TN values, Median 1.87 mg/L. 378 TP values, Median 0.13 mg/L. Waterbody is co-limited by nitrogen and phosphorus based on the Median TN/TP ratio of 13.35 (377 values).

This waterbody is impaired for this parameter based on failing linear vegetation survey results. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient threshold more than once in a three year period, and there is biological evidence indicating non attainment of designated use. This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient threshold more than once in a three year period, and there is biological evidence indicating non attainment of designated use. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and nutrients have been identified as the causative pollutant. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size, and anthropogenic sources have been confirmed using genetic marker and chemical tracer data. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62-303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is not impaired for this parameter because the annual geometric means did not exceed the nutrient threshold more than once in a three year period. WBID 3205B is being added to the Verified List and the department is requesting EPA add it to the 303(d) List based on previous impairment for retired WBID 3205.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period, and there is biological evidence indicating non-attainment of the designated use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period, and there is biological evidence indicating non-attainment of the designated use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

PP=40/41; VP=116/151 Impaired by the IWR threshold and nutrients were found to be the causative pollutant. TN (1.8 mg/L) exceeded the threshold of 1.6 mg/L. TP (0.3 mg/L) exceeded the threshold of 0.22mg/L. BOD (2.0 mg/L) did not exceed the threshold of 2.0 mg/L and had 22 observations. TN/TP median = 6.29, standard deviation 13.35, range 0.22 - 65.2, observations 34. New listing from Cycle 2.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size and is being added to the 303(d) list. PP=457/574; VP=402/503 Impaired by the IWR threshold and nutrients were found to be the causative pollutant. TN (1.9 mg/L) exceeded the threshold of 1.6 mg/L. TP (0.54mg/L) exceeded the threshold of 0.22. BOD (2.0 mg/L) exceeded the threshold of 2.0 mg/L and had 51 observations. TN/TP median = 4.1, standard deviation of 8.02, range of 0.66 - 138.7, observations 412. A TMDL has been proposed by EPA, 9/30/2006.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

PP - Not impaired; VP - Verified impaired. Annual Average Chl-a value exceeded 20 µg/L in 2004 (26.85). 149 TN values, Median 1.66 mg/L. 149 TP values, Median 0.15 mg/L. Waterbody is co-limited by nitrogen and phosphorus based on the Median TN/TP ratio of 10.69 (149 values).

This waterbody is impaired for this parameter based on failing linear vegetation survey results. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient threshold more than once in a three year period, and there is biological evidence indicating non attainment of designated use. This parameter is being added to the 303(d) List. PP = 248 / 396, Potentially impaired; VP = 99 / 158, Impaired. DO met verification threshold of the IWR, and phosphorus and nitrogen are causative pollutants. 207 TN values, Median 1.63 mg/L. 993 TP values, Median 0.42 mg/L. No BOD values. 726 DO values, Median 4.12 mg/L, mean 4.21 mg/L, range 0.00 - 11.62 mg/L.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Based on further analysis by DEP to investigate whether or not the impairment is due to natural conditions, anthropogenic sources could not be ruled out as the cause of the impairment and therefore this parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criteria more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

PP - 0/2 Insufficient Data; VP - 8/25 Verified

PP - No Data; VP - 22/36 Verified This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed using genetic marker and chemical tracer data. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62-303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

PP - No Data; VP - 16/29 Verified

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

PP=53/132; VP=10/30 Natural condition documentation insufficient for EPA approval, therefore this will be assessed as impaired and added to the 303(d) list. A TMDL has been proposed by EPA, 2/23/2005.

PP=87/195; VP=11/15 Natural condition documentation insufficient for EPA approval, therefore this will be assessed as impaired and added to the 303(d) list. A TMDL has been proposed by EPA, 2/23/2005.

PP=90/100; VP=30/30 Natural condition documentation insufficient for EPA approval, therefore this will be assessed as impaired and added to the 303(d) list. A TMDL has been proposed by EPA, 2/23/2005.

PP=81/160; VP=11/20 Natural condition documentation insufficient for EPA approval, therefore this will be assessed as impaired and added to the 303(d) list. A TMDL has been proposed by EPA, 2/23/2005.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size and is being added to the Verified List.

PP=41/101; VP=9/22 Natural condition documentation insufficient for EPA approval, therefore this will be assessed as impaired and added to the 303(d) list. A TMDL has been proposed by EPA, 2/23/2005.

PP=168/222; VP=118/155 Impaired by the IWR threshold and nutrients are found to be the causative pollutant. TN (1.9 mg/L) exceeded the threshold of 1.6 mg/L. TP (0.44 mg/L) exceeded the threshold of 0.22 mg/L. BOD (2.0 mg/L) did not exceed the threshold of 2.0 mg/L and had 22 observations. TN/TP median = 4.4, standard deviation 2.64, range 1.07 - 21.8, observations 181. A TMDL has already been re-proposed by EPA, 9/30/2006.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size and is being added to the 303(d) list. PP=185/236; VP=91/110 Impaired by the IWR threshold and nutrients are found to be the causative pollutant. TN (1.9 mg/L) exceeded the threshold of 1.6 mg/L. TP (0.46 mg/L) exceeded the threshold of 0.22 mg/L. BOD (2.0 mg/L) did not exceed the threshold of 2.0 mg/L and had 16 observations. TN/TP median = 3.8, standard deviation 3.2, range 1.03 - 23.1, observations 132. A TMDL has already been re-proposed by EPA, 9/30/2006.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size and is being added to the Verified List.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size and is being added to the 303(d) list.

PP = 180 / 206; VP = 81 / 99 Impaired by the IWR threshold and nutrients are found to be the causative pollutant. TN (1.9 mg/L) exceeded the threshold of 1.6 mg/L. TP (0.7 mg/L) exceeded the threshold of 0.22mg/L. BOD (3.05 mg/L) exceeded the threshold of 2.0 mg/L and had 12 observations. TN/TP median = 5.5, standard deviation 4.07, range 2.46 - 14.3, observations 14. A TMDL has already been re-proposed by EPA, 9/30/2006.

The annual average Chl-a value exceeded the IWR threshold of 20 µg/L in 2006 (59.73 µg/L). TP (0.07 mg/L) exceeded the threshold of 0.22 mg/L. Data indicate that the WBID is nitrogen limited (TN/TP median = 5.45, standard deviation 4.07, range 2.46 - 14.36, observations 14). A TMDL has already been re-proposed by EPA, 9/30/2006.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size and is being added to the 303(d) list.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

PP = 10 / 10; VP = 21 / 29 Impaired by the IWR threshold and nutrients are found to be the causative pollutant. TN (2.13 mg/L) exceeded the threshold of 1.6 mg/L. TP (0.3 mg/L) exceeded the threshold of 0.22mg/L. BOD (3.3 mg/L) exceeded the threshold of 2.0 mg/L and had 19 observations. TN/TP median = 7.84, standard deviation of 3.5, range, 2.16 - 16.3, observations 27. New listing from Cycle 2.

This waterbody is impaired for this parameter based on failing linear vegetation survey results. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criteria more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired because of beach advisories ≥ 21 days/yr in 2004 and 2005.^

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in a three year period. This parameter is being added to the 303(d) List.

PP = 1 / 6 Insufficient data; VP = 9/ 48 Impaired. VP data have been updated using IWR Run 20.0.

This waterbody is impaired for this parameter based on planning period data and is being added to the 303(d) List. This WBID was created from the retired WBID 3226F that was on the Verified List for this parameter.

This waterbody is impaired for this parameter based on planning period data and is being added to the 303(d) List. This WBID was created from the retired WBID 3226F that was on the Verified List for this parameter.

Impaired based on number of exceedances. This will be added to the 303(d) list.

Impaired based on number of exceedances. This will be added to the 303(d) list.

Impaired based on number of exceedances. This will be added to the 303(d) list. This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in the most recent consecutive three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in the most recent consecutive three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in the most recent consecutive three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in the most recent consecutive three year period. This parameter is being added to the 303(d) List.

Impaired based on number of exceedances. This will be added to the 303(d) list.

PP = 72 / 75; VP = 27 / 27

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the 303(d) List. This waterbody is impaired because the annual average Chl-a value exceeded the listing threshold of 20 µg/L in 2007. Based on TN/TP ratio median of 13.42, TN-TP were identified as co-limiting nutrients. TMDL proposed by EPA 9-30-06. This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the 303(d) List. Verified as impaired based on number of exceedances within the VP and will be added to 303(d) list. Verified as impaired based on number of exceedances within the VP and will be added to 303(d) list. Verified as impaired based on number of exceedances within the VP and will be added to 303(d) list. Verified as impaired based on number of exceedances within the VP and will be added to 303(d) list. Verified as impaired based on 5 exceedances within the VP, and will be added to 303(d) list.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

DO exceeds the listing threshold with TP identified as the causative pollutant. Landuse is estimated to be ~88% anthropogenic.

This waterbody is impaired for this parameter based on failing linear vegetation survey results. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient threshold more than once in a three year period, and there is biological evidence indicating non attainment of designated use. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on failing rapid periphyton survey results. There are at least two temporally independent samples greater than 25% and this parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

Verified as impaired based on data within the VP, added to 303(d) list

PP - 4/17; VP - 6/24. Verified impaired. Nutrients were identified as a causative pollutant based on chlorophyll data/nutrient impairment verification. This waterbody is impaired for this parameter based on failing linear vegetation survey results. This parameter is being added to the 303(d) List.

DO exceeds the listing threshold with TN identified as the causative pollutant. BOD is assessed as DO.

DO exceeds the listing threshold with TN identified as the causative pollutant.

Biochemical oxygen demand is assessed as DO. DO exceeds the listing threshold and TN has been identified as the causative pollutant. EPA completed a TMDL for this WBID in cycle 1 with a 57% reduction required for TBN (total bioavailable nitrogen), a 59% reduction required for TBP (total bioavailable phosphorus) and a 10% reduction required for BOD (biochemical oxygen demand). DO exceeds the listing threshold and TN has been identified as the causative pollutant. EPA completed a TMDL for this WBID in cycle 1 with a 57% reduction required for TBN (total bioavailable nitrogen), a 59% reduction required for TBP (total bioavailable phosphorus) and a 10% reduction required for BOD (biochemical oxygen demand).

This waterbody is impaired for this parameter based on failing linear vegetation survey results. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and nutrients has been identified as the causative pollutant. This parameter is being added to the 303(d) List. Dissolved oxygen grab samples used in this analysis were assessed against a time of day adjustment as described in Rule 62-303.420(9), F.A.C.

This waterbody is impaired for this parameter based on failing linear vegetation survey results. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient threshold more than once in a three year period, and there is biological evidence indicating non attainment of designated use. This parameter is being added to the 303(d) List.

PP = 74 / 245; VP = 38 / 54 Impaired by the IWR threshold and nutrients were found to be the causative pollutant. TN (1.955 mg/L) did exceed threshold of 1.6 mg/L, TN/TP median = 10.990, standard deviation of 4.26, range 5.2241 - 45.14, 801 observations.

The annual average Chl-a values did exceed IWR threshold of 20.0 µg/L in 2002 (20.66 µg/L). TN (1.955 mg/L) did exceed threshold of 1.6 mg/L. TP (0.184 mg/L) did not exceed threshold of 0.22 mg/L. BOD (2.0 mg/L) did not exceed threshold of 2.0 mg/L. Data indicate that the WBID was nitrogen and phosphorous limited (TN/TP median = 10.990, standard deviation of 4.26, range 5.2241 - 45.14, 801 observations). PP = 346 / 566; VP = 225 / 406 Impaired by the IWR threshold and nutrients are found to be the causative pollutant. TN (2.774 mg/L) did exceed threshold of 1.6 mg/L, TN/TP median = 21.085, standard deviation of 11.434, range 5.467 - 75.35, 840 observations.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

PP - 36/115; VP - 32/111

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the 303(d) List. Newly created WBID for Cycle 2. Verified as impaired based on 87 exceedances within the VP, added to 303(d) list.

PP - 83/198; VP - 84/194

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the 303(d) List. Newly created WBID for Cycle 2. Verified as impaired based on data within the VP, added to 303(d) list

PP - 13/56; VP - 20/66

PP - 30/130; VP - 27/130

PP - 41/275; VP - 43/274

PP - 25/142; VP - 28/148

PP - 49/149; VP - 46/145

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the 303(d) List.

PP - 31/136; VP - 40/206. VP data based on IWR Run 20.

PP - 23/13; VP - 25/135

PP - 25/68; VP - 29/70

PP - 29/175; VP - 38/174

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List).

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List).

PP = Insufficient Data; VP = Impaired, with one annual mean Chl-a value above 20 µg/l in 2002, Chl-a mean = 24.571 µg/L. Co-limiting of nitrogen and phosphorus based upon TN/TP ratio. TN median = 1.106 mg/L and TP median = 0.053 mg/L. PP median TN/TP ratio = 18.603 (200 values), VP median TN/TP ratio = 18.603 (114 values). PP = 68 / 121; VP = 47 / 101 Impaired by the IWR threshold and nutrients were found to be the causative pollutant. TN (2.011 mg/L) did exceed threshold of 1.6 mg/L, BOD (2.3 mg/L) did exceed threshold of 2.0 mg/L, TN/TP median = 14.317, standard deviation of 10.035, range 5.213 - 72.82, 107 observations. The annual average Chl-a values did exceed IWR threshold of 20.0 µg/L in 2005 (71.07 µg/L). TN (2.011 mg/L) did exceed threshold of 1.6 mg/L. TP (0.16 mg/L) did not exceed threshold of 0.22 mg/L. BOD (2.3 mg/L) did exceed threshold of 2.0 mg/L. Data indicate that the WBID was nitrogen and phosphorous limited (TN/TP median = 14.317, standard deviation of 10.035, range 5.213 - 72.82, 107 observations).

This parameter is impaired for this waterbody based on the number of exceedances for a sample size less than 20. Fewer than twenty samples may be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a). This parameter is being added to the 303(d) list.

Impaired based on the number of exceedances and will be added to the 303(d) list. New listing from cycle 2.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List. Note, 17 fecal results were excluded from the assessment based on not meeting the holding time "Q" qualified in the verified period.

Impaired based on the number of exceedances and will be added to the 303(d) list. New listing from cycle 2.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This parameter is impaired for this waterbody and was mistakenly excluded from the adopted Cycle 2 Verified List. DO exceeds the IWR threshold with TN and BOD identified as the causative pollutants. Based on TN/TP Ratio Median of 17.69, TN and TP were identified as co-limiting nutrients.

This waterbody is impaired because annual average Chl a (µg/L) values exceeded 20 µg/L in 2002 and 2008. Based on TN/TP Ratio Median of 17.69, TN and TP were identified as co-limiting nutrients.

This waterbody is impaired for this parameter based on failing linear vegetation survey results. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient threshold more than once in a three year period, and there is biological evidence indicating non attainment of designated use. This parameter is being added to the 303(d) List.

PP = 162 / 245; VP = 137 / 203 Impaired by the IWR threshold and nutrients were found to be the causative pollutant. TN (2.816 mg/L) did exceed threshold of 1.6 mg/L, BOD (2.9 mg/L) did exceed threshold of 2.0 mg/L, TN/TP median = 29.939, standard deviation of 20.712, range 7.758 - 192.5, 213 observations. This parameter is impaired for this waterbody because the annual average chlorophyll-a values exceeded the IWR threshold of 20 µg/L in 2006. Based on the median TN/TP ratio of 32.61, total phosphorus is the limiting nutrient. The period of record assessment, which uses all available data regardless of age, indicated potential impairment. However, data older than the verified period were excluded from the final assessment based on the availability of more recent data, and the final assessment was based on the recent data. Dissolved oxygen is impaired and historic chlorophyll-a has insufficient. This parameter will remain on the 303(d) list.

PP = 76 / 164; VP = 69 / 137 Impaired by the IWR threshold and nutrients were found to be the causative pollutant. TN (3.615 mg/L) did exceed threshold of 1.6 mg/L, TN/TP median = 30.3, standard deviation of 11.93, range 8.209 - 63.48, 269 observations. PP = 13 / 60; VP = 7 / 36 Impaired by the IWR threshold and nutrients were found to be the causative pollutant. TN (1.7316 mg/L) did exceed threshold of 1.6 mg/L, TN/TP median = 16.853, standard deviation of 6.627, range 6.99 - 55.51, 568 observations. PP = 71 / 112; VP = 66 / 93 Impaired by the IWR threshold and nutrients were found to be the causative pollutant. TN (3.6125 mg/L) did exceed threshold of 1.6 mg/L, TN/TP median = 40.709, standard deviation of 16.19, range 5.590 - 91.02, 100 observations.

PP = 17 / 35; VP = 1 / 3; Assessment based on Period of Record data,

PP = 62 / 127; VP = 4 / 8; Assessment based on Period of Record data.

PP = 78 / 131; VP = 56 / 104 Impaired by the IWR threshold and nutrients were found to be the causative pollutant. TN (2.12 mg/L) did exceed threshold of 1.6 mg/L, TN/TP median = 24.253, standard deviation of 12.775, range 1.029 - 86.70, 110 observations. PP = 62 / 78; VP = 59 / 73 Impaired by the IWR threshold and nutrients were found to be the causative pollutant. TN (3.342 mg/L) did exceed threshold of 1.6 mg/L, TN/TP median = 35.421, standard deviation of 26.4045, range 11.77 - 150.3, 181 observations.

This waterbody is impaired for this parameter based on failing bioassessments and nutrients have been determined to be the causative pollutant. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter. This parameter was assessed against the minimum nutrient criterion because corrected chlorophyll-a annual geometric means exceeded the applicable chlorophyll-a threshold. The annual geometric means exceeded the nutrient threshold more than once in a three year period. This parameter will be added to the 303(d) list.

This waterbody is impaired for this parameter because the annual arithmetic means exceeded the criteria more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size and is being added to the 303(d) list.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on failing linear vegetation surveys with a C of C < 2.5 and FLEPPC percent coverage of > 25%. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size and is being added to the 303(d) list. This WBID was created from retired WBID 3258C1 which was on the Verified List for this parameter.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size and is being added to the 303(d) list.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size and is being added to the 303(d) list.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and nutrients have been identified as the causative pollutant. This parameter is being added to the Verified List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter because the annual arithmetic means exceeded the criterion more than once in a three year period during the verified period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This parameter is impaired for this waterbody based on the number of exceedances for a sample size less than 20. Fewer than twenty samples may be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a) F.A.C. This parameter is being added to the 303(d) list.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size and is being placed in category 5 based on the previous assessment of retired WBID 3258H1. This WBID was created from retired WBID 3258H1 which was on the Verified List for this parameter. Total nitrogen, total phosphorous, and biochemical oxygen demand median values are not elevated relative to comparable waters for identification of a causative pollutant. Nutrients were identified as the causative pollutant in the previous assessment. The period of record assessment, which uses all available data regardless of age, indicated potential impairment. However, data older than the verified period were excluded from the final assessment based on the availability of more recent data, and the final assessment was based on the recent data. This parameter is being added to the 303(d) list.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size and is being added to the 303(d) list.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter because the annual arithmetic means exceeded the criterion more than once in a three year period during the verified period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter because the annual arithmetic means exceeded the criteria more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This parameter is impaired for this waterbody based on the number of exceedances for the sample size and is being added to the 303(d) list. This WBID was created from retired WBID 3259B which was on the Verified List for this parameter.

This parameter is impaired for this waterbody because the shellfish harvesting classification is not fully approved by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture and Consumer Services. This parameter is being added to the 303(d) list.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. The waterbody includes at least one sampling location (21FLCOLLBARRIVN and 21FLCOLLFAKAUPOI) that has a median fecal coliform MPN value that exceeds 14 counts per 100 ml for the verified period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size. Total nitrogen exceeded its threshold of 1.6 mg/L and was found to be the causative pollutant. The period of record assessment, which uses all available data regardless of age, indicated potential impairment. However, data older than the verified period were excluded from the final assessment based on the availability of more recent data, and the final assessment was based on the recent data. This parameter will remain on the 303(d) list.

This waterbody is impaired because the annual average Chl-a value exceeded the listing threshold of 20.0 µg/L in 2002 and 2008. Based on TN/TP ratio median of 8.63, TN was identified as the limiting nutrient. New listing from cycle 2.

This waterbody is impaired for this parameter based on failing bioassessments and nutrients have been determined to be the causative pollutant. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. This parameter was assessed against the minimum nutrient criterion because corrected chlorophyll-a annual geometric means exceeded the applicable chlorophyll-a threshold. The annual geometric means exceeded the nutrient threshold more than once in a three year period. This parameter will be added to the 303(d) list.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient threshold more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody is impaired because the annual average Chl-a value exceeded the listing threshold of 20.0 µg/L in 2002, 2007, and 2008. Based on TN/TP ratio median of 10.55, TN was identified as the limiting nutrient.

This waterbody is impaired because the annual average Chl-a value exceeded the listing threshold of 20.0 µg/L in 2003 and 2008. Based on TN/TP ratio median of 5.85, TN was identified as the limiting nutrient.

PP = Insufficient Data; VP = Impaired, with one annual mean Chl-a value above 20 µg/L in 2002, Chl-a mean = 27.825 µg/L. Co-limiting of nitrogen and phosphorus based upon TN/TP ratios [TN median = 0.95 mg/L and TP median = 0.1595 mg/L., VP median TN/TP ratio = 5.87 (10 obs.).

Impaired based on number of exceedances and BOD was found to be the causative pollutant. Excluded from period of record assessment, as it has been determined with more recent data that the WBID is impaired.

PP = 679 / 932; VP = 411 / 598 Impaired by the IWR threshold and nutrients were found to be the causative pollutant. TN (1.693 mg/L) did exceed threshold of 1.6 mg/L, TN/TP median = 133.66, standard deviation of 117.791, range 10.38 - 667.3, 510 observations. Impaired based on number of exceedances. This will be added to the 303(d) list. VP: Chl-a values exceeded IWR threshold hold in 1998 (28.18 µg/L), 1999 (29.42 µg/L), 2000 (16.3 µg/L), 2001 (14.04 µg/L) and 2004 (26.27 µg/L). Data indicate that the WBID is co-limited (TN/TP Median = 13.818, standard deviation of 8.7913, range of 5.609 - 62.0, 88 observations). Data based on updated Run 22 from 10-26-05.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

Impaired based on number of exceedances. This will be added to the 303(d) list.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Data quality assurance issues were brought to the attention of the department by Collier County for all metal results analyzed by EPA 200.7 and 200.8 from July 27, 2017 to June 30, 2018. These results have been excluded from the assessment for the following organizations: 21FLCOMI, 21FLCCZM, 21FLCOLL and 21FLNAPL. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criteria more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is listed as impaired for this parameter because the shellfish harvesting classification is not fully approved by the Shellfish Harvest Area Classification Program of the department of Agriculture and Consumer Services. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criteria more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter because the annual geometric means exceeded the criteria more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size and is being added to the 303(d) list.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size and is being added to the 303(d) list. This WBID was created from retired WBID 3278R which was on the Verified List for this parameter.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size and is being added to the 303(d) list. This WBID was created from retired WBID 3278R which was on the Verified List for this parameter. This parameter is impaired for this waterbody based on the number of exceedances for a sample size less than 20 and is being added to the 303(d) list. Fewer than twenty samples may be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a) F.A.C. This WBID was created from retired WBID 3278R which was on the Verified List for this parameter.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size and is being added to the 303(d) list. This WBID was created from retired WBID 3278R which was on the Verified List for this parameter. This parameter is impaired for this waterbody based on the number of exceedances for the sample size and is being added to the 303(d) list. This WBID was created from retired WBID 3278R which was on the Verified List for this parameter.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. The waterbody includes at least one sampling location (21FLNAPLNBAY29, 21FLNAPLNBAYBV, and 21FLNAPLNBAYNL) that has a median fecal coliform MPN value that exceeds 14 counts per 100 ml for the verified period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This parameter is impaired for this waterbody based on the number of exceedances for the sample size and is being added to the 303(d) list. This WBID was created from retired WBID 3278R which was on the Verified List for this parameter. This parameter is impaired for this waterbody based on the number of exceedances for the sample size and is being added to the 303(d) list. This WBID was created from retired WBID 3278R which was on the Verified List for this parameter.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and nutrients have been identified as the causative pollutant. This parameter is being added to the Verified List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criteria more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

pp = 163 / 365; vp = 158 / 397. TN is the causative pollutant with TN Median = 0.78 mg/L (364 obs). Listed as impaired on Cycle 1 Verified List.

pp = 7 / 18; vp = 11 / 31 Impaired This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Data quality assurance issues were brought to the attention of the department by Collier County for all metal results analyzed by EPA 200.7 and 200.8 from July 27, 2017 to June 30, 2018. These results have been excluded from the assessment for the following organizations: 21FLCOMI, 21FLCCZM, 21FLCOLL and 21FLNAPL. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

Impaired based on number of exceedances. This will be added to the 303(d) list.

PP = 30 / 334; VP = 27 / 202

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the 303(d) List.

PP = 18 / 69; VP = 14 / 46

Impaired based on number of exceedances. This will be added to the 303(d) list.

This parameter is being added to the Group 4-Cycle 2 Verified List based on meeting verification requirements for impairment. This waterbody was delisted in Cycle 2 in error. The initial assessment indicated an insufficient number of fish were analyzed, however additional information was received confirming a sufficient number of fish were analyzed.

PP = 22 / 109; VP = 22 / 72

Impaired based on number of exceedances. This will be added to the 303(d) list. Impaired based on number of exceedances. This will be added to the 303(d) list.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the 303(d) List.

pp = 4 / 5; vp = 15 / 32. DO met verification threshold of IWR, and BOD was identified as a causative pollutant. PP - median TN = 0.80 mg/L (n=3), median TP = 0.02 mg/L (n=3), no BOD data. VP - median TN = 0.96 mg/L (n=32), median TP = 0.02 mg/L (n=34), median BOD = 2.2 mg/L (n=31). This waterbody is impaired for nutrients based on information indicating an imbalance in flora or fauna; it is being added to the Verified List and the department is requesting EPA add it to the 303(d) List pursuant to Rule 62- 303.450(2), F.A.C. Studies performed by the University of South Florida Water Institute and the department have found a shift from a diverse, native macrophyte-based system to one dominated by periphyton and more invasive macrophyte species.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the criterion more than once in a three-year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

pp = 3 / 4; vp = 7 / 15. DO met verification threshold of IWR, and BOD was identified as a causative pollutant. PP - median TN = 1.31 mg/L (n=4), median TP = 0.205 mg/L (n=4), no BOD data. VP - median TN = 1.38 mg/L (n=16), median TP = 0.089 mg/L (n=16), median BOD = 2.6 mg/L (n=12).

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear, alkaline lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear, alkaline lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size, and anthropogenic sources have been identified using genetic marker and chemical tracer data. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62-303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

pp = 2 / 8; vp = 7 / 24

Listed due to downgrade in shellfish harvesting classification.

This parameter is impaired for this waterbody. The waterbody includes at least one sampling location that has a median fecal coliform MPN value that exceeds 14 counts per 100 ml for the verified period. This parameter is being added to the 303(d) list.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. The waterbody includes seven sampling locations that have median fecal coliform MPN values that exceed 14 counts per 100 ml in the verified period; these are stations 21FLSEAS28SEAS201 (MED=37), 21FLSEAS28SEAS202 (MED=35), 21FLSEAS28SEAS207 (MED=41.5), 21FLSEAS28SEAS244 (MED=48.5), 21FLSEAS28SEAS246 (MED=45), 21FLSEAS28SEAS428 (MED=42), 21FLSEAS28SEAS430 (MED=24) and 21FLSEAS28SEAS435 (MED=29). This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is listed as impaired for this parameter because the shellfish harvesting classification is not fully approved by the Shellfish Harvesting Area Classification Program of the Department of Agriculture and Consumer Services. This parameter is being added to the Verified List and the Department is requesting EPA add it to the 303(d) List. This waterbody was placed in category NA in the previous assessment cycle, but EPA deferred action on approving the assessment to allow for additional review.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

pp = 19 / 35; vp = 27 / 38 DO met verification threshold of IWR, TN, TP and BOD were identified as causative pollutants. PP - median TN = 5.1 mg/L (n=41), median TP = 1.812 mg/L (n=41), median BOD = 10.2 mg/L (n=37). VP - median TN = 3.83 mg/L (n=29), median TP = 0.87 mg/L (n=29), median BOD = 6.6 mg/L (n=30). EPA established a TMDL in 2007.

pp = 23 / 35; vp = 19 / 30. EPA established a TMDL in 2007.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the annual geometric mean 2005-2013 exceeding the criterion more than once in a three year period. This parameter is being added to the 303(d) List.

pp = 3 / 3; vp = 22 / 35. DO met verification threshold of IWR, and TP and BOD were identified as a causative pollutants. PP median TN = 0.99 mg/L (n=27), median TP = 0.26 mg/L (n=27), median BOD = 3.2 mg/L (n=2). VP median TN = 1.0 mg/L (n=24), median TP = 0.12 mg/L (n=25), median BOD = 2.2 mg/L (n=24).

pp = 12 / 48; vp = 7 / 26

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

pp = 4 / 9; vp = 17 / 35 This parameter is impaired for this waterbody based on the number of exceedances for the sample size. Biochemical oxygen demand (BOD) was identified as the causative pollutant because it exceeded the BOD threshold for identification of a causative pollutant (2.0 mg/L). The period of record assessment, which uses all available data regardless of age, indicated potential impairment. However, data older than the verified period were excluded from the final assessment based on the availability of more recent data, and the final assessment was based on the recent data. This parameter is being added to the Verified List and the 303(d) list.

pp = 2 / 2; vp = 10 / 20. DO met verification threshold of IWR, and BOD was identified as a causative pollutant. PP - no TN data, no TP data, no BOD data. VP - median TN = 1.10 mg/L (n=16), median TP = 0.093 mg/L (n=19), median BOD = 2.6 mg/L (n=19). pp = 5 / 21; vp = 5 / 21 pp = 7 / 16; vp = 8 / 26. TMDL established by EPA 5/7/2007. pp = 2 / 3; vp = 8 / 11. TN median exceeded the threshold for streams in the verified period but was based on only 5 samples (10 are required). PP - no TN data, no TP data, median BOD = 2 mg/L (n=1). VP - median TN = 2.10 mg/L (n=5), median TP = 0.099 mg/L (n=5), median BOD = 2 mg/L (n=8). Linked to algal mats.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size, and anthropogenic sources have been identified based on percent anthropogenic landuse. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62-303.390(2)(f) F.A.C. There is a DEP Adopted Fecal Coliform TMDL. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size, and anthropogenic sources have been identified based on percent anthropogenic landuse. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62-303.390(2)(f) F.A.C. There is a DEP Adopted Fecal Coliform TMDL. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size, and anthropogenic sources have been identified based on percent of anthropogenic landuse. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62-303.390(2)(f) F.A.C. There is a DEP Adopted Fecal Coliform TMDL. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size, and anthropogenic sources have been identified based on percent of anthropogenic landuse as well as using chemical tracer data. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.390(2)(f) F.A.C. There is a DEP Adopted Fecal Coliform TMDL. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size, and anthropogenic sources have been identified. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

This parameter is impaired for this waterbody. The waterbody includes at least one sampling location that has a median fecal coliform MPN value that exceeds 14 counts per 100 ml for the verified period. This parameter is being added to the 303(d) list.

This parameter is impaired for this waterbody because the shellfish harvesting classification is not fully approved by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture and Consumer Services. This parameter is being added to the 303(d) list.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and will remain on the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criteria more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the criterion more than once in a three-year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is listed as impaired for this parameter because the shellfish harvesting classification is not fully approved by the Shellfish Harvesting Area Classification Program of the Department of Agriculture and Consumer Services. This parameter is being added to the Verified List and the Department is requesting EPA add it to the 303(d) List.

This waterbody is listed as impaired for this parameter because the shellfish harvesting classification is not fully approved by the Shellfish Harvesting Area Classification Program of the Department of Agriculture and Consumer Services. This parameter is being added to the Verified List and the Department is requesting EPA add it to the 303(d) List.

This parameter is impaired for this waterbody. The waterbody includes at least one sampling location that has a median fecal coliform MPN value that exceeds 14 counts per 100 ml for the verified period. This parameter is being added to the 303(d) list. This parameter is impaired because the shellfish harvesting classification is not fully approved by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture and Consumer Services. It is being added to the 303(d) list. This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and will remain on the 303(d) List. This parameter is impaired because the shellfish harvesting classification is not fully approved by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture and Consumer Services. It is being added to the 303(d) list. This parameter is impaired for this waterbody. The waterbody includes at least one sampling location that has a median fecal coliform MPN value that exceeds 14 counts per 100 ml for the verified period. This parameter is being added to the 303(d) list. This parameter is impaired because the shellfish harvesting classification is not fully approved by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture and Consumer Services. It is being added to the 303(d) list.

pp = 1 / 3; vp = 21 / 23. DO met verification threshold of IWR, and TN and BOD were identified as causative pollutants. PP - median TN = 1.94 mg/L (n=3), median TP = 0.025 mg/L (n=3), no BOD data. VP - median TN = 14 mg/L (n=27), median TP = 0.05 mg/L (n=27), median BOD = 6.5 mg/L (n=25).

This waterbody is impaired for this parameter based on failing bioassessments and nutrients have been determined to be the causative pollutant. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient threshold more than once in a three year period, and there is biological evidence indicating non-attainment of the designated use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed using genetic marker and chemical tracer data and indenitified using land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size and will remain on the 303(d) list.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

PP = 7 / 19; VP = 7 / 26. EPA established a TMDL on 11/27/2006. This parameter is impaired for this waterbody based on the number of exceedances for a sample size less than 20. Fewer than twenty samples may be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a), F.A.C. Total nitrogen and biochemical oxygen demand were identified as the causative pollutants because they were elevated relative to comparable waters (exceeded 1.03 mg/L for TN and 2.0 mg/L for BOD). The period of record assessment, which uses all available data regardless of age, indicated potential impairment. However, data older than the verified period were excluded from the final assessment based on the availability of more recent data, and the final assessment was based on the recent data. This parameter is being added to the 303(d) list.

This waterbody is impaired for this parameter based on failing bioassessments and nutrients have been determined to be the causative pollutant. A stressor identification study identified nutrients and a low dissolved oxygen condition contributing to the impairment. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period, and there is biological evidence indicating non-attainment of the designated use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria more than once in a three year period, and there is biological evidence indicating non-attainment of the designated use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been confirmed using genetic marker and chemical tracer data. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62-303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size, and anthropogenic sources have been confirmed using landuse analysis. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62- 303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List. This waterbody is impaired for this parameter because there were 21 days or more of beach advisories in the verified period. This is a beach WBID, which are assessed solely on beach advisory information received from DOH.^ This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter because there were 21 days or more of beach advisories in the verified period. This is a beach WBID, which are assessed solely on beach advisory information received from DOH.^ This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

This waterbody is listed as impaired for this parameter because the shellfish harvesting classification is not fully approved by the Shellfish Harvest Area Classification Program of the department of Agriculture and Consumer Services. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

This parameter is listed as impaired because the shellfish harvesting classification is not fully approved by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture. This parameter is being added to the 303(d) list.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

This parameter is listed as impaired because the shellfish harvesting classification is not fully approved by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture. This parameter is being added to the 303(d) list.

This waterbody is impaired for this parameter based on failing bioassessments and nutrients have been determined to be the causative pollutant. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient threshold more than once in a three year period, and there is biological evidence indicating non-attainment of the designated use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter based on failing rapid periphyton survey results. There are at least two temporally independent samples greater than 25% and this parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient threshold more than once in a three year period, and there is biological evidence indicating non-attainment of the designated use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and anthropogenic sources have been identified using land use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a) F.A.C. Based on further analysis by DEP to investigate whether or not the impairment is due to natural conditions, anthropogenic sources could not be ruled out as the cause of the impairment and therefore this parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size and is being added to the 303(d) list.

PP = 7 / 13; VP = 7 / 18

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear, alkaline lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear, alkaline lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear, alkaline lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List. Listed as impaired based on shellfish harvesting classification of prohibited by Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture. WBID 548A was retired to form two new WBIDs (548AA and 548AC) because portions of the original WBID are Class II (shellfish harvesting) and portions are Class III. WBID 548AA contains the areas that are Class III, while WBID 548AC contains the Class II waters.

Listed as impaired based on shellfish harvesting classification of prohibited by Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture. DEP corrected this WBID classification from Class III to Class II.

Listed as impaired based on shellfish harvesting classification of prohibited by Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture. The WBID boundary was adjusted to include all of the Class II designated area.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in a consecutive three year period. This parameter is being added to the 303(d) List.

Beach advisories > 21 days/yr for 2001-2004.

Listed as impaired based on shellfish harvesting classification of prohibited by Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture. WBID 548G was retired to form two new WBIDs (548AA and 548AC), because portions of the original WBID are Class II (shellfish harvesting) and portions are Class III.

This parameter exceeds the listing threshold. WBID 548G was retired to form two new WBIDs (548AA and 548AC), because portions of the original WBID are Class II (shellfish harvesting) and portions are Class III.

Listed as impaired based on shellfish harvesting classification of prohibited by Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear, alkaline lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear, alkaline lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter based on failing bioassessments and nutrients have been determined to be the causative pollutant. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear, acidic lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear, acidic lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear, acidic lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This parameter is impaired for this waterbody based on the number of exceedances for a sample size less than 20. Fewer than twenty samples may be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a), F.A.C. The period of record assessment, which uses all available data regardless of age, indicated potential impairment. However, data older than the verified period were excluded from the final assessment based on the availability of more recent data, and the final assessment was based on the recent data. This parameter is being added to the 303(d) list.

This waterbody is impaired for this parameter based on failing bioassessments and nutrients and specific conductance have been determined to be the causative pollutants. A stressor identification study identified nutrients, specific conductance, and a low dissolved oxygen condition contributing to the impairment. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter based on the number of exceedances for the sample size and nutrients have been identified as the causative pollutant. Samples used in this analysis were assessed against a time of day adjustment as described in 62-303.420(9), F.A.C. This parameter is being added to the Verified List and will remain on the 303(d) List.

This waterbody is impaired for this parameter based on two or more failing rapid periphyton surveys with >25% coverage of periphyton. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criterion more than once in a three year period, and there is biological evidence indicating non-attainment of the designated use. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on failing rapid periphyton survey results. There are at least two temporally independent samples greater than 25% and this parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in the most recent consecutive three year period. This parameter is being added to the 303(d) List. There is additional data for this waterbody in ENRH7 and ENRH8 as shown below. ENRH7 (AGM) 2009 (0.1 µg/L) 2010 (0.2 µg/L) 2011 (0.2 µg/L) 2012 (0.2 µg/L) 2013 (0.2 µg/L) 2014 (0.1 µg/L) 2015 (0.4 µg/L) ENRH8 (AGM) 2009 (0.1 µg/L) 2010 (0.2 µg/L) 2011 (0.2 µg/L) 2012 (0.1 µg/L) 2013 (0.2 µg/L) 2014 (0.2 µg/L) 2015 (0.3 µg/L)

PP = No Data; VP = 42 / 86

PP = No Data; VP = 5 / 8. Assessment based on Period of Record data

PP = No Data; VP = 21 / 29 PP = No Data; VP = 19 / 47 PP = No Data; VP = 8 / 21 PP = No Data; VP = 5 / 19 PP = No Data; VP = 9 / 31 PP = No Data; VP = 7 / 14 This parameter is impaired for this waterbody based on the number of exceedances for this sample size and will be added to the 303(d) list.

PP = No Data; VP = 8 / 13 This waterbody is impaired for this parameter based on the number of exceedances for the sample size, and anthropogenic sources have been identified based on percent of anthropogenic landuse. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This parameter is impaired because it exceeds the listing threshold.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a) F.A.C. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear, acidic lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear, acidic lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear, acidic lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear, alkaline lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear, alkaline lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This parameter exceeds the listing threshold and will be added to the 303(d) List.

PP = 2 / 3; VP = 14 / 24

PP = 1 / 43; VP = 23 / 55

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in the most recent consecutive three year period. This parameter is being added to the 303(d) List.

This WBID is impaired because there were 21, or greater, days of beach advisories in 2002 through 2007. Beach WBID assessment is based on beach advisory information received from DOH. ^

Listed as impaired based on shellfish harvesting classification of prohibited by Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture. WBID 701 was retired to form two new WBIDs (701A and 701B) because portions of the original WBID are Class II (shellfish harvesting) and portions are Class III. WBID 701B contains the areas that are Class III, while WBID 701A contains the Class II waters.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This parameter exceeds the listing threshold and will be added to the 303(d) List. This waterbody is impaired for this parameter based on the number of exceedances for the sample size, and anthropogenic sources have been identified using genetic marker and chemical tracer data. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62-303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This parameter exceeds the listing threshold and will be added to the 303(d) List.

Beach advisories > 21 days/yr for 2002 and 2003.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size, and anthropogenic sources have been confirmed using genetic marker and chemical tracer data. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62-303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in a three year period. This parameter is being added to the 303(d) List.

Beach advisories > 21 days/yr for 2002 - 2003.

This parameter exceeds the listing threshold and will be added to the 303(d) List. This parameter is impaired for this waterbody based on the number of exceedances for a sample size less than 20. Fewer than twenty samples may be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a), F.A.C. The period of record assessment, which uses all available data regardless of age, indicated potential impairment. However, data older than the verified period were excluded from the final assessment based on the availability of more recent data, and the final assessment was based on the recent data. This WBID was created from the retired WBID 746 that was on the Verified List for this parameter. This parameter is being added to the 303(d) list.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This WBID is impaired because there were 21, or greater, days of beach advisories in 2003, 2004, 2005, and 2007. Beach WBID assessment is based on beach advisory information received from DOH. ^

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear, acidic lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear, acidic lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter. The annual geometric means exceeded the nutrient criteria for a clear, acidic lake more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size and is being added to the 303(d) list. This WBID was created from the retired WBID 756 which was on the 1998 303(d) list and the Verified List for this parameter. This waterbody is impaired for this parameter based on the number of exceedances for the sample size, and anthropogenic sources have been identified using genetic marker and chemical tracer data. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62-303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter based on the number of exceedances for the sample size, and anthropogenic sources have been identified using genetic marker and chemical tracer data. Fewer than twenty samples can be used to identify a waterbody as impaired if there are at least five exceedances, per 62-303.390(2)(f) F.A.C. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

PP = 35 / 1090; VP = 27 / 474. This WBID was listed because there was a downgrade in the shellfish harvesting classification (from approved to conditionally approved) for some portion of this Class II waterbody.

This parameter exceeds the listing threshold and will be added to the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in the most recent consecutive three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in the most recent consecutive three year period. This parameter is being added to the 303(d) List.

This WBID is impaired because there were 21, or greater, days of beach advisories in 2004 and 2007. Beach WBID assessment is based on beach advisory information received from DOH. ^

Beach advisories > 21 days/yr for 2003.

This waterbody is impaired for this parameter because there were 21 days or more of beach advisories in 2012-2015. This is a beach WBID, which are assessed solely on beach advisory information received from DOH.^ This parameter is being added to the 303(d) List.

This parameter was originally listed as verified impaired on the Cycle 1 Verified List, but was delisted by amendment on February 7, 2012, because the prohibited classification is due to administrative reasons. However, this waterbody also contains some shellfish harvesting areas that are not fully approved not due to administrative reasons by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture; therefore this parameter is being added to the 303(d) list. This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in a three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in the most recent consecutive three year period. This parameter is being added to the 303(d) List.

This parameter was originally listed as verified impaired on the Cycle 1 Verified List, but was delisted by amendment on February 7, 2012, because the prohibited classification is due to administrative reasons. However, this waterbody also contains some shellfish harvesting areas that are not fully approved not due to administrative reasons by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture; therefore this parameter is being added to the 303(d) list.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. The waterbody includes at least one sampling location that has a median fecal coliform MPN value that exceeds 14 counts per 100 ml for the verified period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in the most recent consecutive three year period. This parameter is being added to the 303(d) List.

This WBID is impaired because there were 21, or greater, days of beach advisories 2006. Beach WBID assessment is based on beach advisory information received from DOH. ^

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and total nitrogen has been identified as the causative pollutant. This parameter is being added to the 303(d) list.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in a three year period. This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in the most recent consecutive three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in the most recent consecutive three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in the most recent consecutive three year period. This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and nutrients have been identified as the causative pollutant. This parameter is being added to the 303(d) list. Dissolved oxygen grab samples used in this analysis were assessed against a time of day adjustment as described in Rule 62-303.420(9), F.A.C.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in the most recent consecutive three year period. This parameter is being added to the 303(d) List.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size and is being added to the 303(d) list.

This parameter is impaired for this waterbody. The waterbody includes at least one sampling location that has a median fecal coliform MPN value that exceeds 14 counts per 100 ml for the verified period. This parameter is being added to the 303(d) list. This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and will remain on the 303(d) List.

This waterbody is impaired for this parameter based on two or more failing rapid periphyton surveys with >25% coverage periphyton. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List. This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter because there were 21 days or more of beach advisories in the verified period. This is a beach WBID, which are assessed solely on beach advisory information received from DOH.^ This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter because there were 21 days or more of beach advisories in 2012-2013. This is a beach WBID, which are assessed solely on beach advisory information received from DOH.^ This parameter is being added to the 303(d) List.

This WBID is impaired because there were 21, or greater, days of beach advisories in 2004 and 2007. Beach WBID assessment is based on beach advisory information received from DOH. ^

This WBID is impaired because there were 21, or greater, days of beach advisories in 2005, 2007, and 2008. Beach WBID assessment is based on beach advisory information received from DOH. ^

This waterbody is impaired for this parameter because there were 21 days or more of beach advisories in 2013. This is a beach WBID, which are assessed solely on beach advisory information received from DOH.^ This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter because there were 21 days or more of beach advisories in 2012. This is a beach WBID, which are assessed solely on beach advisory information received from DOH.^ This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter because there were 21 days or more of beach advisories in 2012-2013. This is a beach WBID, which are assessed solely on beach advisory information received from DOH.^ This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter because there were 21 days or more of beach advisories in 2012. This is a beach WBID, which are assessed solely on beach advisory information received from DOH.^ This parameter is being added to the 303(d) List.

Beach advisories > 21 days/yr for 2003.

This waterbody is impaired for this parameter because there were 21 days or more of beach advisories in 2011. This is a beach WBID, which are assessed solely on beach advisory information received from DOH.^ This parameter is being added to the 303(d) List.

Beach advisories > 21 days/yr for 2003.

This waterbody is impaired for this parameter because there were 21 days or more of beach advisories in 2011. This is a beach WBID, which are assessed solely on beach advisory information received from DOH.^ This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter because there were 21 days or more of beach advisories in 2012. This is a beach WBID, which are assessed solely on beach advisory information received from DOH.^ This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter because there were 21 days or more of beach advisories in 2011. This is a beach WBID, which are assessed solely on beach advisory information received from DOH.^ This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter because there were 21 days or more of beach advisories in 2012. This is a beach WBID, which are assessed solely on beach advisory information received from DOH.^ This parameter is being added to the 303(d) List. This waterbody is impaired for this parameter because there were 21 days or more of beach advisories in 2011. This is a beach WBID, which are assessed solely on beach advisory information received from DOH.^ This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter because there were 21 days or more of beach advisories in the verified period. This is a beach WBID, which is assessed solely on beach advisory information received from DOH.^ This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This parameter is impaired because the shellfish harvesting classification is not fully approved by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture and Consumer Services. This parameter is being added to the 303(d) list.

Beach advisory posted for a total of 33 days in 2001, 61 days in 2002, 106 days in 2003, 91 days in 2004, 300 days in 2005, and 92 days in 2006

Beach advisory posted for a total of 28 days in 2001, 38 days in 2002, 108 days in 2003, 83 days in 2004, 229 days in 2005, and 140 days in 2007

This waterbody is listed as impaired for this parameter because the shellfish harvesting classification is not fully approved by the Shellfish Harvest Area Classification Program of the department of Agriculture and Consumer Services. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criteria more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criteria more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This parameter is impaired because the shellfish harvesting classification is not fully approved by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture and Consumer Services. It is being added to the 303(d) list. This waterbody is impaired for this parameter because the annual geometric means exceeded the criteria more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter because the annual geometric means exceeded the criteria more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter because the annual geometric means exceeded the criteria more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is listed as impaired for this parameter because the shellfish harvesting classification is not fully approved by the Shellfish Harvesting Area Classification Program of the Department of Agriculture and Consumer Services. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

Listed due to downgrade in shellfish harvesting classification.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. Stations 21FLSEAS34SEAS100 (east of island with fish shack) and 21FLSEAS34SEAS110 (park beach near Hwy 40) had a median value that exceeded the 14 counts/100 mL criterion with at least 20 samples in the verified period. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

This waterbody is listed as impaired for this parameter because the shellfish harvesting classification is not fully approved by the Shellfish Harvest Area Classification Program of the department of Agriculture and Consumer Services. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in a three year period during the verified period. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in a three year period for station 21FLWQA 34SEAS110 during the verified period. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List 21FLWQA 34SEAS110.

This parameter is listed as impaired because the shellfish harvesting classification is not fully approved by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture. This parameter is being added to the 303(d) list.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size and is being added to the 303(d) list.

This parameter is listed as impaired because the shellfish harvesting classification is not fully approved by the Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture. This parameter is being added to the 303(d) list.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in a three year period during the verified period. There was an outlier in the data for 2016 that caused a higher value in the AGM. This did not affect the assessment because the AGM still exceeded the criterion with the outlier removed. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in a three year period during the verified period. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List. pp = Not impaired; vp = Impaired. The waterbody segment exceeded the 21- day threshold for closures, advisories, or warnings in 2002 (64 days), 2003 (154 days), 2004 (122 days), and 2005 (147 days) as per IWR Rule 62- 303.360(1)(c). This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in a three-year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter because there were 21 days or more of beach advisories in the verified period. This is a beach WBID, which are assessed solely on beach advisory information received from DOH.^ This parameter is being added to the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criteria more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in a three year period. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. Listed on Cycle 1 Verified List based on change in shellfish harvesting classification (Downgraded from approved to conditional). Current classification effective as of September 28, 2004 Conditionally Approved. This WBID is meant to include shellfish downgrades for the Ten Thousand Islands shellfish harvesting area.

This parameter is impaired for this waterbody because the annual average chlorophyll-a values exceeded the IWR threshold for streams of 20 µg/L in 2010. Based on the median TN/TP ratio of 5.4, total nitrogen is the limiting nutrient. This parameter is being added to the 303(d) list.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in a three year period during the verified period. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

Beach advisories > 21 days/yr in 2002, 2003, 2004, 2005, and 2006.

Beach advisories > 21 days/yr in 2002, 2003, 2005, and 2006.

Beach advisories > 21 days/yr in 2002, 2004, 2005, and 2006. This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in a three year period during the verified period. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This parameter is impaired for this waterbody based on the number of exceedances for the sample size and is being added to the 303(d) list.

PP = 21 / 31; VP = 22 / 38 DO met verification thresholds of IWR, and BOD was identified as a causative pollutant. PP no TN, TP, BOD data. VP median TN= 0.93mg/L (n=27), median TP= 0.0755mg/L (n=28), median BOD= 2.7mg/L (n=28).

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in a three year period during the verified period. This parameter is being added to the Verified List and the department is requesting EPA add to the 303(d) List.

Beach advisories > 21 days/yr in 2001, 2005, and 2006.

This parameter is impaired for this waterbody because there were 21 days, or more, of beach advisories in 2005 and 2008. This is a beach WBID, which are assessed solely on beach advisory information received from DOH.^ This parameter will be added to the 303(d) list.

This waterbody is impaired for this parameter because the annual geometric means exceeded the criterion more than once in the most recent consecutive three year period. This parameter is being added to the 303(d) List.

PP = 0 / 2; VP = 14 / 24

Listed as impaired based on shellfish harvesting classification of prohibited by Shellfish Environmental Assessment Section (SEAS) of the Department of Agriculture.

Beach advisories > 21 days/yr for 2002 and 2003.

This waterbody is verified as impaired for this parameter based on the number of exceedances (6) for a sample size less than 20. Fewer than twenty samples may be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a). This parameter is being added to the 303(d) list. WBID 872 was retired to form two new WBIDs: 872A and 872B to create fresh and estuarine segments.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. This waterbody is impaired for this parameter based on the number of exceedances for the sample size. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

PP = 2 / 5; VP = 11 / 26 DO met verification thresholds of IWR, and BOD was identified as a causative pollutant. PP no TN, TP, BOD data. VP median TN= 0.8185mg/L (n=22), median TP= 0.028mg/L (n=26), median BOD= 2.95mg/L (n=24).

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size. The waterbody includes at least one sampling location that has a median fecal coliform MPN value that exceeds 14 counts per 100 ml for the verified period. This parameter is being added to the 303(d) List.

This parameter is impaired for this waterbody based on the number of exceedances for a sample size less than 20. Fewer than twenty samples may be used to identify a waterbody as impaired if there are at least five exceedances, per Rule 62-303.420(7)(a), F.A.C. This WBID was created from the retired WBIDs 863 and 883 that were not on the Verified List for this parameter. This parameter is being added to the 303(d) list.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size, and anthropogenic sources have been identified using genetic marker and chemical tracer data. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

PP = 0 / 2; VP = 7 / 22

WBID did not meet the Class II water quality criteria for fecal coliforms because the median value for the verified period exceeded 14 MPN/100 mL.

Beach advisories > 21 days/yr for 2004.

Beach advisories > 21 days/yr for 2003-2004.

Beach advisories > 21 days/yr for 2003-2004.

PP = 2 / 8; VP = 9 / 28. EPA established a TMDL on 11/27/2006.

This parameter exceeds the listing threshold and will be added to the 303(d) List.

PP = 1 / 1; VP = 13 / 21

This waterbody is impaired for this parameter based on the number of exceedances for the sample size, and anthropogenic sources have been identified using genetic marker and chemical tracer data. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on the number of exceedances for the sample size and is being added to the 303(d) List.

This waterbody is impaired for this parameter based on DOH fish consumption advisory data from 2012 for 20 Bluegill with an average arsenic concentration of 0.018 mg/kg. This parameter is being added to the Verified List and the department is requesting EPA add it to the 303(d) List. PP = 2 / 3; VP = 14 / 20