COASTAL SALMON SPAWNING SURVEY
PROCEDURES MANUAL
2005
OREGON ADULT SALMONID INVENTORY AND SAMPLING PROJECT (OASIS)
OREGON DEPARTMENT OF FISH AND WILDLIFE Table of Contents
OREGON ADULT SALMONID INVENTORY AND SAMPLING PROJECT ...... 1
COASTAL CHINOOK RESEARCH AND MONITORING PROJECT...... 2
THE OREGON PLAN FOR SALMON AND WATERSHEDS...... 3
MAP OF THE OREGON COAST SHOWING MAJOR RIVERS, LOCATIONS OF SPAWNER SURVEY CREWS, AND FISHERY AND WATERSHED MANAGEMENT DISTRICTS...... 4
SALMON SPAWNING SURVEYOR ID LIST ...... 6
SUPPLY LIST FOR SPAWNING SURVEYORS ...... 10
SURVEY SITES...... 11
SURVEY DESCRIPTION LIST (EXAMPLE) ...... 13
SPAWNING SURVEY DESCRIPTION CHANGE FORM...... 14
RANDOM SURVEY SITE VERIFICATION FORM (EXAMPLE)...... 15
RANDOM SURVEY SITE MAP EXAMPLE...... 17
LANDOWNER CONTACTS ...... 18
REPEAT SURVEY LANDOWNER CONTACT FORM (EXAMPLE) ...... 20
FISH IDENTIFICATION ...... 24
FIN NOMENCLATURE OF SALMON ...... 25
SPAWNING SURVEY FIELD FORMS ...... 31
SPAWNING SURVEY DATA FORM ...... 32
2005 SPAWNER SURVEY DATA FORM INSTRUCTIONS ...... 33
BIOLOGICAL SAMPLING FORM ...... 39
BIOLOGICAL SAMPLING FORM (BSF) INSTRUCTIONS...... 40
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CODED WIRE TAG AND FIN-MARK RECOVERIES ...... 45
2005 SNOUT ID LABELS ...... 46
SCALE SAMPLING...... 47
DNA SAMPLING ...... 50
SPAWNING SURVEY EVALUATION FORM 2005...... 51
INSTRUCTIONS: SALMON SPAWNING SURVEY EVALUATION FORM ...... 52
DESCRIPTION OF COHO SALMON SPAWNING GRAVEL...... 53
METHOD OF ESTIMATION OF COHO SPAWNING GRAVEL...... 54
GENERAL SURVEY INSTRUCTIONS...... 55
FIRST WEEK PRIORITIES...... 56
DEALING WITH SPECIAL CIRCUMSTANCES...... 57
CELL PHONES ...... 58
PUBLIC RELATIONS AND SAFETY ...... 59
STATE VEHICLES ...... 60
PERSONNEL POLICIES AND PROCEDURES...... 61
LIST OF NORTH COAST DISTRICT SURVEYS ...... 67
LIST OF TILLAMOOK DISTRICT SURVEYS ...... 70
LIST OF MID-COAST DISTRICT SURVEYS ...... 73
LIST OF UMPQUA DISTRICT SURVEYS...... 76
LIST OF COOS-COQUILLE DISTRICT SURVEYS ...... 79
LIST OF SOUTH COAST DISTRICT SURVEYS ...... 82
LIST OF UPPER ROGUE DISTRICT SURVEYS...... 85 iii
OREGON ADULT SALMONID INVENTORY AND SAMPLING PROJECT
The Oregon Adult Salmonid Inventory and Sampling (OASIS) project is the branch of the Oregon Department of Fish and Wildlife (ODFW) with the primary task of monitoring the status of naturally produced coastal and lower Columbia salmonid stocks. Stock status is monitored through spawning surveys conducted throughout coastal watersheds. Spawning fish surveys are conducted in cooperation with district biologists located in four different watershed management districts. Data generated by the project are used by State and Federal natural resource agencies in the management of Oregon's salmon resource. These data are integral in assessing progress in the Oregon Plan for Salmon and Watersheds (Oregon Plan).
PROJECT OBJECTIVES
Four species of salmonids are monitored through spawning surveys. Primary objectives for each of these species are as follows:
Coho Salmon
• Estimate population size of natural spawners. • Evaluate straying and natural spawning by hatchery fish. • Map the spatial distribution of spawners. • Monitor Threatened and Endangered stocks. • Monitor and assess abundance trends. • Integrate EMAP assessment: spawners-habitat-juveniles. • Evaluate compliance with the ODFW Native Fish Conservation Policy. • Develop and assess fishery harvest regulations.
Chinook Salmon
• Develop monitoring methods that estimate spawner escapement. • Monitor and assess abundance trends. • Determine life history. • Evaluate compliance with the ODFW Native Fish Conservation Policy.
Chum Salmon
• Monitor and assess abundance trends. • Develop and implement monitoring programs of additional coastal stocks. • Evaluate compliance with the ODFW Native Fish Conservation Policy.
Steelhead
• Monitor and assess annual trends in abundance and distribution • Complete the fourth year of coast-wide monitoring (winter-spring 2006).
Additional project information is available on our web site at: http://www.orst.edu/Dept/ODFW
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COASTAL CHINOOK RESEARCH AND MONITORING PROJECT
ODFW is continuing a multi-year study designed to develop methods that provide reliable estimates of fall chinook spawner escapements for Oregon coastal streams. Funding for this study was obtained through a U.S. Letter of Agreement and is administered by the Chinook Technical Committee (CTC) of the Pacific Salmon Commission. The CTC is responsible for evaluating the rebuilding process of naturally spawning chinook stocks covered by the Pacific Salmon Treaty, and is comprised of scientists from the Northwest and Canada. This project is in direct response to requirements set forth by recent amendments to the Pacific Salmon Treaty and the adaptation of an Aggregate Abundance-based Management (AABM) strategy for mixed stock fisheries. This management strategy provides a means for sharing conservation responsibility of far-north migrating stocks originating from Oregon watersheds and subsequently intercepted in commercial fisheries off Canada and Southeast Alaska.
The AABM model requires precise escapement estimates for selected “indicator” basins. These basins are assumed to represent the ocean distributions exhibited by coastal Oregon chinook salmon stocks as well as their genetic diversity. There are basically two objectives to achieve during the spawning season. The first is an accurate and precise escapement estimate in each of the indicator basins selected. The second objective is to develop an unbiased survey design that best correlates with actual spawner abundance. The goal of this project is to provide yearly escapement estimates, and to identify a survey design that can be used to estimate spawner abundance for coastal streams in the future. By using indicator stocks to calibrate the survey methodology the survey-based estimates can be adjusted to yearly variations in climate, run strength, and regional effects.
Chinook assessment studies will be conducted in the Siletz and Siuslaw river basins and a proportion of chinook in the Coquille will be radio-tagged. These radio tagged fish will be easily identified by the presence of a wire protruding from their mouth and an anchor tag near the dorsal fin. Mark-recapture studies in the Siletz and Siuslaw will be conducted to obtain an estimate of fall chinook populations in each of these river basins. Various survey methods will be used to provide an estimate of spawner abundance in the tributary and mainstem spawning habitats. These include a random survey design where data is collected on live fish as well as carcasses, and carcass mark-recapture in mainstem habitat. Surveyors in the Siuslaw should pay special attention to adipose clipped chinook and all snouts should be recovered. Surveyors in all of these basins will follow the same survey protocol used elsewhere with the addition of recognizing and recording the existence of operculum punches and collecting radio tags.
Chinook will be captured using entanglement nets, seines or weirs in the tidewater (freshwater) areas. Once captured, these fish will be marked by having holes punched through their operculum. Marks will be stratified by Julian week and identified by the side of fish and area of operculum punched. The second capture event will consist of recovering chinook on the spawning grounds. All fish will be sampled for length, scales and sex, and checked for marks. Careful attention should be directed towards identifying opercule punches. Carcasses may fungus up or the punch may skin over making it difficult to see the mark. The gill cover may erode into the punch, changing the round hole to a crescent shape mark. Any remnant of an opercule punch will be recorded as a marked fish. Each fish will be sampled once and the tail removed. Surveyors will use both foot and boat surveys to locate carcasses.
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THE OREGON PLAN FOR SALMON AND WATERSHEDS
A Unique Foundation
The Oregon Plan represents a unique foundation – Oregon’s coordinated approach – to recover salmonid populations and restore watersheds to healthy conditions, and to address the issues and requirements of the federal Clean Water- and Endangered Species Acts. The Oregon Plan is designed to function within the state’s regulatory requirements, social realities, and funding constraints. Four legs support the foundation of the Oregon Plan: action by government agencies, including a regulatory baseline; voluntary action; monitoring; and scientific oversight.
Government Agencies
Action by government agencies, including enforcement of a regulatory baseline, is the first leg of the Oregon Plan. State and Federal agencies have committed to accomplish work that will complement work on private lands, helping sustain and restore healthy watersheds, improve water quality, and recover native salmonids across the landscape.
Voluntary Action
Voluntary action is the second leg of the Oregon Plan. Although more than half of Oregon is publicly owned, the distribution of public and private lands in Oregon and the life cycle requirements of federally-listed salmonid species, combine to make water quality and watershed health on private lands crucial to meeting requirements of federal Clean Water- and Endangered Species Acts. This is where voluntary action by Oregonians fits. Private landowners – individuals and industries, rural and urban landowners, businesses, and citizens – are filling critical gaps by conducting restoration work essential to watershed health, clean water, and recovery of listed fish species. Much of this work is coordinated through local watershed councils.
Monitoring
Monitoring is the third leg of the Oregon Plan. The goal of the monitoring effort is to document the current condition of Oregon’s key watershed health parameters, track changes over time, and determine if restoration efforts are effective. The spawning surveys that you will be conducting are a key component of this monitoring activity.
Scientific Oversight
Scientific oversight is the final leg of the Oregon Plan. The Independent Multidisciplinary Science Team (IMST) has an integral role in this process. This aspect provides a foundation that includes independent evaluation of Oregon Plan actions, monitoring and management programs, as well as a commitment to conduct needed research.
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Map of the Oregon coast showing major rivers, locations of spawner survey crews, and Fishery and Watershed Management Districts.
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OREGON ADULT SALMONID INVENTORY & SAMPLING FLOW CHART
Coastal Districts Scale Project Management Biologists CWT Processing Lisa Borgerson Coastal Chinook Project Bill Murray Kanani Bowden Life Cycle Monitoring Project 50 Spawning Surveyors
CWT Database Management Fish Division John Leppink OASIS Project - Crew Chiefs Vacant – Lower Columbia Dave Stewart – North Coast Josh Edwards – Eugene/Umpqua Pat Burns – South Coast Oregon Plan Ocean Fisheries Management
Non-governmental NOAA Fisheries OASIS - CORVALLIS Organizations Partner Agencies Mark Lewis – Acting Project Leader Briana Sounhein - Coho Erik Suring – Lower Columbia Gary Susac - Steelhead LaNoah Babcock – Data QA & Entry Public
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SALMON SPAWNING SURVEYOR ID LIST
CREW LOCATION ID NUMBER SURVEYOR
CLACKAMAS 91 Casey Myers 93 Cathy Geweke 113 Alex Neerman 112 Sheila Davis 13 Eric Brown (Acting LC Crew Chief)
SAUVIES ISLAND 71 Lucas Lawerence 41 Lisa Willett
ASTORIA 50 Erin Donnelly 97 Zach Forster
SEASIDE 98 Scott Kirby 111 Katie Voelke
JEWEL 116 Mark Jessop 118 Anson Friar 114 Scott Venables 115 Seth Ring
NEHALEM 119 Tim Dalton HATCHERY 122 Ben Walczak 121 Trevor Diemer 22 Scott Young
TILLAMOOK 20 Michael Sinnott 21 Jessie Waite 110 Ethan Guzman 23 Jeff Johnson
CORVALLIS 11 Mark Lewis 01 Dave Stewart (North Crew Chief) 02 Briana Sounhein 03 Gary Susac 04 Erik Suring 05 Edward Hughes 46 Jon Kluck 08 Pat Burns (South Crew Chief) 10 LaNoah Babcock 09 Kelly Moore
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SALMON SPAWNING SURVEYOR ID LIST (continued)
CREW LOCATION ID NUMBER SURVEYOR
NEWPORT 35 Serina Adams 31 Lawerence Gangle III 32 Kevin Kemper 34 Bill Ratliff 37 Lincoln SWDC Surveyors 38 Watershed Council Surveyors 39 Steve Johnson and crew 33 Newport District Staff
EUGENE 40 Michael Scheu 42 John Elliot 06 Matt Johnson 49 Brent Reed 007 Joshua Edwards (Middle Crew Chief)
MAPELTON 47 Jon Nott 48 Mike Thalhaueser
REEDSPORT 96 Sabrina Derusseau 51 Sharon Sanders
ROSEBURG 55 Melanie O’Hara 53 Kevin Drake 57 Heather Wise 58 Summer Cross 117 Greg Huchko 45 Holly Truemper 52 District Staff
COOS BAY 30 Peter Cole 61 Paul Bubrick 62 Neil Jensen 63 Eric Himmelreich 79 Jay Scelza 70 Nathaniel Davis 67 Bruce Miller’s Crew 68 Industry Surveyors 69 Watershed Council
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SALMON SPAWNING SURVEYOR ID LIST (continued)
CREW LOCATION ID NUMBER SURVEYOR
GOLD BEACH 94 Greg Ryder 65 ?? 72 Broodstock Crew 73 Elk River Crew 74 All Volunteers
GRANTS PASS 86 Supervisory Fishery Biologist
Chinook Program
SALMON RIVER 308 Jim Mick 309 Jodiah Smith
SIUSLAW 300 Sandy Kennedy 301 Jennifer Hulett 302 Robert Lee 303 Shari Anderson 304 Justin Miles 305 Steven Clark 306 Frank Drake 307 Tina Gomez
SILETZ 315 Billy Wilson 316 Robin Miranda 317 Ryan Easton 318 Ben Soeby 319 Jessica Vogt 320 Yens Lovtang 321 Kelly Corbett 322 Pete Gruendike
AT LARGE 324 Brian Riggers 323 Chris Stephens 325 Jane Hatfield 326 Matt Powell 327 Other
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Miscellaneous
BLM 100 All Surveyors
FOREST SERVICE 200 All Surveyors
CURRY COUNTY WATERSHED COUNCIL 400 All Surveyors
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SUPPLY LIST FOR SPAWNING SURVEYORS Forms:
1. Salmon Spawning Survey Form 2005. 2. Landowner Contact Form. 3. Description Change Form. 4. Biological Sampling Form with Snout ID Tabs. 5. Spawning Survey Evaluation Form. 6. List of Survey Location Descriptions. 7. Report of Operations Form.
Equipment:
1. Chest waders, with belt. 2. Wading shoes and neoprene booties. 3. Polarized sunglasses. 4. Raincoat. 5. Hat. 6. Orange field vest. 7. Pencils, red pen, and Sharpies. 8. Spawning Fish Survey Field Notebook. 9. Measuring tape (in millimeters). 10. Forceps for scale collection. 11. Scale envelopes. 12. DNA sample tray and scissors 13. Knife with sheath. 14. Snout / Fin-mark ID Labels. 15. Snout bags. 16. Wading staff with gaff. 17. Signs for marking boundaries of surveys. 18. C. B. Radio (as needed). 19. Life Jacket (For River Surveys, as needed). 20. Spawning Survey Procedures Manual. 21. GPS unit (as needed). 22. Site maps (coverage, topographic, road, GIS, State Forestry, etc.). 23. Cell Phone. 24. Machete.
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SURVEY SITES
Description Lists
You will receive a list of descriptions for surveys in your area which provide detailed directions to the survey site, including the name of the stream to be surveyed, geographic data, and the UTM coordinates for the start and end points (see example, page 13). This information will allow you to determine the boundaries of the site you need to survey.
Verify that you are in the right place and that signs are correct. Sometimes Reach ID's and/or segment numbers change and signs need to be updated. If signs are missing, first check to make sure that you have correctly identified the start and/or end point. Then check the landowner comments to see if someone has asked us not to post signs. Correct the sign if you are confident of your changes. Some of the surveys you will be walking have not been visited in as long as 12 years. Update the description where necessary.
Description Changes
If there are any changes to be made, such as correcting UTM coordinates, assigning a different segment number, or placing a sign in another location, reflect them on the Survey Description Change Form (page 14). Fill out the form completely. When writing the description, be detailed and precise. Proper grammar and legibility are important. After reading the descriptions to your surveys you'll get an idea of what makes a good description.
Maps
You will also be provided with a map showing all of the surveys in your area. Additional materials may be available if you cannot find a site using the description and the map. Summer surveyors fill out a Survey Site Verification Form when they set up a new survey (pages 15-16). Surveys set up since 1996 usually have a 1:24,000 topographic map with the start and end points marked. In addition, the verification form may have specific comments on landmarks or landowners that might help you locate the start and/or end points of the survey.
UTM Coordinate System
This is an easy to use coordinate system, based on a projection of the earth as a flat surface. The earth is divided into 60 zones. All of western Oregon falls within Zone 10. Within each zone there are two coordinates that define a point: a northing (x) and an easting (y). The northing coordinate indicates the distance in meters from the southern boundary of Zone 10 (the values increase as you move north). The easting coordinate indicates the distance from the western boundary of Zone 10 (the values increase as you move east). These coordinates correspond to distances, in meters, inside the zone boundary. Most maps will have the UTM grid printed on them, some of the older maps may only have ticks, and thus the grid must be constructed. In the margins of the map, next to the grid lines are the coordinates for the boundaries of the 1000-meter grid. The two larger digits are called the “principal digits” and are always in ten thousands and thousands of meters.
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Instructions for GPS Units
Turn the unit on by pressing the button with the red light bulb. You will get a screen that says "Acquiring EPE" showing the relative positions of all satellites the unit can detect, the relative strength of each signal, and a battery gauge. The black outline around each satellite will disappear as the unit obtains a lock on it. If you have trouble getting a strong enough signal, try moving to a clear area - out from under tree cover and as far away from hills as possible. Moving up a hillside out of the creek gorge or holding the unit high in the air sometimes helps.
When the unit gets a lock on enough satellites it will switch to another screen that shows a compass on the top. The UTM coordinates are shown on the lower left-hand corner of this screen (10T=Easting coordinate, UTM=Northing coordinate).
The "Page" button will scroll through several different screens. The settings should be correct, but if you need to change them, go to the "Main Menu" screen. Use the large pad in the middle to scroll up or down until "System Menu" is highlighted. Press "Enter". The "System" setup will allow you to change the screen contrast. Use the large pad to scroll to the setting you wish to change and press "Enter". Use the scroll key to change the setting and then press "Enter" again to save your settings. If the unit refuses to lock satellites, check these settings.
Press page to go back to the "Main Menu" screen. The settings for "Navigation" should be set to: POSN: UTM/UPS DATUM: NAD27 CONUS CDI SCALE: ±0.25 UNITS: STATUTE HEADING: Auto Mag E018
To get an accurate UTM reading, stand in desired location, wait for satellites to lock in, and then push the “mark” button. In this new screen, use the large center pad to scroll down to “average” and then press “enter.” Either hold still or put the unit on the ground until the “FOM” number at the bottom left stabilizes (about one minute). Once the FOM has stabilized, write the UTM’s shown near the center of the screen down. To turn the unit off, hold down the button with the red light bulb for about 3 seconds.
Be sure to carry extra batteries for the GPS Unit
Missing UTM’S
You will need to obtain UTM coordinates for all surveys where they are missing, and for surveys that were last surveyed prior to 2000. The crew chiefs will be rotating GPS units through the crews to establish missing UTM's. Write new or corrected UTM’s on the Spawner Survey Form (page 31), crossing out incorrect or outdated UTM’s on this form where applicable. Highlight the changes on the copied sheet prior to sending the data in!
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SURVEY DESCRIPTION LIST (Example) REACH SEG- BASIN SUBBASIN SURVEY LOCATION ( T,R,S; DESCRIPTION ID MENT DOWNSTREAM UTMs; UPSTREAM UTMs)
22137.00 2 COOS RIVER MAIN STEM WILSON CR T26S R12W 29 FROM COOS BAY, GO SOUTH ON HWY 101 TO A SIGN THAT SAYS SUMNER/GOLF COURSE. TURN LEFT AT THE DIAMOND WOOD PRODUCTS MILL AND GO 4.6 MILES TO THE BUSHNELLS HOUSE (4640- BROWN). PARK AND WALK ALONG THE BUSHNELLS PASTURE FENCELINE TO WILSON CR (NO SIGN POSTED). SURVEY FROM HERE UPSTREAM 1.0 MILES TO CARDWELL CREEK ON THE LEFT (SIGN ON WILLOW ON LEFT). EXIT VIA ROAD ON LEFT. ***NOTE: BRING MACHETE AND DO NOT GO DOWNSTREAM OF THE FENCELINE ON THE BUSHNELLS PROPERTY; THE MESSERLES ON THE RIGHT SIDE OF THE CREEK DENIED ACCESS.
22140.00 1 COOS RIVER MAIN STEM PANTHER CR T26S R12W 33 FROM TOWN OF SUMNER DRIVE SOUTHEAST ON COOS BAY WAGON RD. 1.3 MILES TO PULLOUT ON RIGHT ACROSS ROAD FROM A GREEN GATED 4791503 0408387 GRAVEL ROAD. PARK AND ENTER WILSON CR. FROM THE SOUTH END 4791608 0408730 OF THE PULLOUT. WALK UPSTREAM 50M TO MOUTH OF PANTHER CR. LEFT (START SIGN TREE LEFT). FROM MOUTH SURVEY UPSTREAM .32 MILES TO END POINT 50 M ABOVE END SIGN (END SIGN ON DOWN LOG CENTER.) EXIT VIA SURVEY.
22141.00 1 COOS RIVER MAIN STEM WILSON CR T26S R12W 33 FROM SUMNER, DRIVE EAST 1.4 MILES AND PARK AT PANTHER CR CROSSING. WALK DOWN TO THE MOUTH OF PANTHER CR. SURVEY WILSON CR FROM THE CONFLUENCE WITH PANTHER CR (SIGN ON ALDER ON THE LEFT) UPSTREAM 0.49 MILES TO A TRIBUTARY ON THE LEFT JUST PAST A ROAD CROSSING (SIGN ON TREE ON LEFT). EXIT VIA THE ROAD ON THE LEFT.
22141.30 1 COOS RIVER MAIN STEM WILSON CR, T27S R12W 04 FROM THE TOWN OF SUMNER AT THE SUMNER STORE, DRIVE EAST 1.85 TRIB D MILES TO A DRIVEWAY ON THE RIGHT. WILSON CREEK, TRIB D IS 10 METERS UPSTREAM OF THE DRIVEWAY. SURVEY TRIB D FROM THE MOUTH (SIGN ON MAPLE ON LEFT) UPSTREAM 0.53 MILES TO TWO EQUAL SIZE TRIBS (SIGN ON AN ALDER ON THE LEFT). EXIT VIA SURVEY. ***NOTE: WINTER SURVEYORS SHOULD DETERMINE IF COHO COULD GO ABOVE THE ENDPOINT IN EITHER BRANCH.
22141.70 1 COOS RIVER MAIN STEM WILSON CR T26S R12W 33 PARK AT LAST DRIVEWAY UPSTREAM ON SUMNER-FAIRVIEW RD. (FROM SUMNER) WHERE THE ROAD CROSSES PANTHER CR. ACCESS WILSON CR, 5 METERS FROM THE ROAD, AND SURVEY FROM THE CONFLUENCE WITH PANTHER CR (SIGN ON TREE ON LEFT) UPSTREAM 0.48 MILES TO A JUNCTION OF THREE TRIBUTARIES FEEDING WILSON CR (SIGN POSTED ON NEAREST TREE, 50 METERS DOWNSTREAM FROM ENDPOINT). EXIT VIA SURVEY AREA.
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SPAWNING SURVEY DESCRIPTION CHANGE FORM
DATE ______SURVEYOR ID ______
DISTRICT ______
BASIN ______
SUBBASIN ______
REACH ______.
SEGMENT
MAP COORDINATES: (at downstream end of survey segment)
TOWNSHIP T RANGE R SECTION
(Change UTM’s on the Spawner Survey Form)
DESCRIPTION: (Print legibly, use complete sentences, and observe standard rules of grammar. Include as much detail as necessary so that your description will enable future surveyors to locate exactly the same stream segment. Try to avoid using landmarks and names that are likely to change over time.)
______(use reverse to continue). Check one of the following boxes
Description changed during: coho season (October – January) steelhead season (January – May)
14 RANDOM SURVEY SITE VERIFICATION FORM (EXAMPLE)
Page 1
15 RANDOM SURVEY SITE VERIFICATION FORM (EXAMPLE)
Page 2
16 RANDOM SURVEY SITE MAP EXAMPLE
17 LANDOWNER CONTACTS
You must contact landowners for permission before conducting surveys that are located on private land. You will be given pre-printed LANDOWNER CONTACT FORMS (page 20) for all surveys. The data on these forms is our best knowledge about the landowners on the survey, but it is not infallible. People buy, sell and subdivide land, and there may be new landowners that are not on your sheet, or old landowners that no longer live on the survey that need to be removed.
When you contact landowners, introduce yourself in a professional manner and identify your organization. Explain your reason for being there, and be clear on your intent, methods, and the frequency of your visits. Inform landowners that surveys will be conducted through January, and where noted, through May to accommodate steelhead spawning surveys. Be aware that some landowners may have been contacted previously by other projects.
An information pamphlet discussing the Oregon Plan for Salmon and Watersheds is also available for the landowner’s information (page 21-22). This pamphlet gives an overview of the goals of the Oregon Plan and also explains the adult, juvenile, and habitat projects of ODFW and the stream health-biotic index project of DEQ. Be sure to check the box next to the Adult Salmon Spawning Surveys section of the pamphlet prior to handing it out.
¾ Record your contacts on the Landowner Contact Form: • Write in any additional landowners that don't appear on the form with as much contact data as you can obtain (address, phone, etc.). • Edit and highlight any landowner information that is incorrect. • If there are a lot of corrections to be made, please use a blank Contact Form.
¾ Verify the information: • Make sure the names, complete address, and phone number(s) are all correct: • If this information is incorrect, record the correct information on the landowner contact form and highlight them so they may be updated in our database. • If the landowner lives offsite, record the situs address in the comments section. • Obtain the tax lot information if it is not provided.
¾ Check the most recent OK date: • Landowners that gave permission during survey verifications this summer do not need to be contacted again unless there are specific instructions to do so in the landowner comments or the survey description. • If the target species includes steelhead obtain permission through the end of May. • If the list does not indicate that a corporate landowner has been contacted, obtain permission from the crew chief before conducting the survey. • If the contact person is different from the owner or organization name, two names will be listed under the “Name” field separated by a dash. The first is the owner name and the second is the contact person.
¾ Record the date landowners were contacted: • Once a landowner has given permission, fill in the date under "New OK date". Do NOT just checkmark the box, write “yes” or “no”, or leave blank! • If a landowner denies permission, note this under "Comments" and do not trespass on their property. You may need to drop a survey if this occurs - consult your crew chief.
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¾ Enter “Yes” or “No” in the “Data Requested” column: • Do NOT enter a check mark or leave this column blank! • If “Yes”, make sure you have the current address of the owner (including the zip code).
¾ Check the "Comments" section for any special instructions: • Accommodate any special requests and write them down (i.e., the owner requests that surveyors not park in the driveway). You can’t have too much information!
¾ Submit the Form to your Crew Chief: • When you have obtained all the necessary permissions, write your surveyor ID in the "Contacts Complete by Surveyor ID" checkbox. • Complete this part of the form even when there are no landowner contacts that need to be made (for example, if the survey falls entirely on public land). • Do not wait to turn this in!
19 LANDOWNER CONTACT FORM 2005 CONTACTS COMPLETED BY SURVEOR ID: Return completed form to Corvallis by November 15 for data entry. You may want to keep a copy for your own use. You do not need to contact landowners that already have a 2005 OK-date EXCEPT when there is a note in the comments or the description asking you to drop by again. Update landowners and contact information, record OK date for all private landowners, and indicate any data requests. Organize your comments and write
SURVEY TYPE AND TARGET SPECIES: DISTRICT Upper Rogue SURVEY NAME Sams Cr RANDOM STEELHEAD BASIN Rogue River REACH ID 20944.00 RANDOM COHO SUBBASIN Mainstem SEGMENT 1 Name Address City State ZIP Phone Phone 2 Previous New OK Data Tax Lot# Comments Date Date Req
Erwin & Rhonda 9399 John Day Dr. Gold Hill OR 97525- 11/5/2002 No 305 Need driveway access for start point. Falk Code to gate 1940. *Recontact for permission to access gate and property. Ron & Debbie 7133 Ramsey Rd.Gold Hill OR 97525 (541) 855-2015 11/3/2003 No 101 Anderson Bureau of Land 3040 Biddle Rd.Medford OR 97504- 541-618-2200 10/23/2002 Yes 300 Management - 4180 Ron Wenker John Setzer 420 Sams Cr. Rd.Gold Hill OR 97525 (541) 855-1770 11/3/2003 Yes 509, 500 Please call prior to each survey. He was somewhat reluctant to grant permission. Claude 100 Sams Cr. Rd.Gold Hill OR 97525 541/855-9882 11/3/2003 No 402 if someone is home stop by Garayalde Fred Schulzke 9415 John Day Dr.Gold Hill OR 97525 (541) 855-9269 11/3/2003 No 506 Another number you can try is (541)855- 9299. Judy Anderson 11144 Hwy 234 Gold Hill OR 97525- 11/10/2003 No 200
Beverly Schulzke 11983 Hwy 234 Gold Hill OR 97525- 11/6/2003 No 403 P.O Box 302
20 Landowner Contacts Page _____ of _____
Year:______Date: / /
Reach ID: ______Segment: County: ______
Township - Range: ______ID Num:______Surveyor:______
Plat # / Tax lot # Name: Site Address: ______Address:
Phone: ( ) -
Email address:______Data Requested: Yes / No OK'd Date: ______
Plat # / Tax lot # Name: Site Address: ______Address:
Phone: ( ) -
Email address:______Data Requested: Yes / No OK'd Date: ______
Plat # / Tax lot # Name: Site Address: ______Address:
Phone: ( ) -
Email address:______Data Requested: Yes / No OK'd Date: ______Sampling Record What is the Oregon Plan? Oregon Plan for The Oregon Plan for Salmon and Stream Name: Watersheds is a broad-based Salmon and Site Number: effort of citizens, local watershed Field Crew: groups, the State of Oregon, and federal agencies to restore
healthy salmon populations and Agency: their watersheds.
Local Phone: The most important part of the Supervisor: Plan is the idea that people Phone: working together, with the support of state and local Comments: government, can do more to help fish than could be Watersheds accomplished by a strict regulatory approach. Stream Monitoring Example of sample sites in the Mid-Coast The Plan has been in effect for about three years. Hundreds of 2005-2006 projects designed to improve stream habitat and watershed The Oregon Plan Monitoring Program is conditions have been completed. designed to assess the current status of fish Support for watershed groups, populations and their habitat and to SWCD’s, and landowners has document the effectiveness of restoration brought people together to and enhancement programs. develop stream restoration plans tailored to the needs of the local Streams in your area have been randomly community. selected to census salmon populations, conduct habitat surveys, and assess overall For more information: stream health. Sampling is coordinated Oregon Plan for Salmon and using an unbiased statistical survey plan. Watersheds Specially trained field crews conduct the Streams are randomly selected for sampling Program Office (503) 378-3589 x821 various sampling tasks described in this using a computer program. Landowner Monitoring Program: (503) 986-0181 pamphlet. names and addresses are not used in reports or data summaries. If you would like Internet Address: www.oregon-plan.org a copy of the report summary for your area, we will gladly supply it without charge.
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Monitoring Program Activities Contacts: Oregon Department of Fish and Stream Habitat Assessment Wildlife (ODFW) Stream habitat surveys are conducted from These Oregon Plan Monitoring Projects are Kelly Moore (541) 757-4263 x226 June through September in one-half mile designed to work together to give us basic Briana Sounhein (541) 757-4263 x227 long sections of stream. Each section takes information on salmon populations and Erik Suring (541) 757-4263 x264 about a day to survey. Surveyors will collect conditions across large geographic areas. information on channel size, flow, substrate composition, large wood, habitat complexity, Activities that we would like to conduct on Juvenile Salmon Population and riparian characteristics. the stream or streams on your property are Census marked in the checkbox by the name of each project. Divers will snorkel pool habitats to count juvenile salmon. Over time, these counts Adult Salmon Spawning Surveys help us understand trends in the abundance Counts of spawning adult salmon are a key and distribution of juvenile salmonids. At indicator of abundance. A team of one or some of the sites, more precise population two surveyors will visit each potential site estimates will be made for juvenile coho, once during the summer to mark the cutthroat, and steelhead. boundaries of the survey and collect data on stream size, availability of spawning gravel, Contact: ODFW and possible barriers to fish-passage. Kim Jones (541) 757-4263 x260
Stream Health – Biotic Index Measurement
Measurements of aquatic insects, aquatic Survey sites will vary in length. Field crews plants, water quality, fish communities, and will spend about one day at each site over the habitat are combined to create and integrated summer sampling period. assessment of stream condition. Contact: ODFW The length of stream sampled ranges from Kevin Leader – Mid and North Coast about one-quarter to one-half a mile. Crews Each survey covers about one mile of stream. (541) 757-4263 x263 spend a day at each site. Starting with the fall spawning migration, Dave Jeppsen – Rogue and South Coast and continuing through early winter, crews (541) 757-4263 x263 Contact: Oregon Department of will visit each site about once a week to Environmental Quality count the salmon. Greg Pettit (503) 229-5983
FISH IDENTIFICATION
You will be expected to identify the species of live fish and the species and gender of carcasses encountered in the field. To accomplish this you will use a number of characteristics including size, run timing, geographic location, coloration, body morphology, markings, and behavior. It is prudent to use as many characteristics as possible when designating species and gender.
Chinook appear in early fall, and are generally much larger than coho. They tend to spawn in bigger water, and are typically darker than coho with bronze to black coloration. Some chinook (especially large males) are quite red, but never anterior to the dorsal fin. You can distinguish reddish chinook from coho by their size. They have large irregular spots on their backs and both lobes of their tails, and their tail rays are smooth. Chinook can often be distinguished by the white 'skunk-line' of fin rot on their backs. The gums at the base of their teeth are black.
Coho appear later than chinook - generally beginning in late October to early November. They tend to spawn in smaller streams and are smaller fish. They are dull to bright red with greenish backs, and can often be distinguished by the white spot on the operculum behind their eyes. Occasionally you may see a coho that still has its bright silver ocean coloration. They tend to be deeper in the body, making them look football-shaped. They have small round spots on their backs and the upper lobe of their tails. The gums at the base of their teeth are white, but the rest of the jaw is dark. They tend to be more shy than chinook and are easily startled.
Chum appear almost exclusively in the northern part of the coast. They don't travel far in-river and tend to spawn in low gradient streams within a few miles of the ocean. They can be distinguished by the distinctive striated bars on their sides. They have very small speckles on their backs. Other key characteristics include their large eyes and lack of spotting on the tail.
Steelhead appear in the winter and early spring. They are more elongated (torpedo-shaped) than salmon, and have a broader caudal peduncle and a square tail (salmon tails are more lobed or forked). They are gray-blue on their backs and silvery-white on their lower halves. They have completely white mouths, small spots on their tails, and are very shy. In order to observe them you must move quietly and stealthily.
Females tend to have a more extensively eroded tail fin from digging the redd - both lobes are eroded evenly. Males have a more pronounced kype and are generally larger overall. The lower lobe of a male's tail is usually more eroded than the upper lobe. If you are unsure of the gender of a carcass, you can cut open its belly to examine its gonads.
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FIN NOMENCLATURE OF SALMON
Key Area
MEPS Length
Axillary Appendage
Schematic diagram of a generic salmon identifying fin names, the location of the Key Area for scale sampling and the start and end points for measuring the Mid-Eye to Posterior Scale (MEPS) length.
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CHINOOK (Oncorhynchus tshawytscha)
Chinook salmon (Oncorhynchus tshawytscha) are the largest of Oregon’s five salmon species and are often referred to as King Salmon because of their size and power. Fall Chinook in our coastal rivers and streams, range in size from about 21 to 47 inches (jacks are less than 20 inches) and 20 to 60 pounds at the time of spawning.
Although the majority of chinook salmon head to sea a few months after they emerge from the gravel, some remain in their home stream for one or two years. Chinook returning to spawn vary greatly in age, in Oregon three, four and five-year-old chinook are most common. Further north, five, six and seven-year-olds are more abundant. Chinook jacks are two- or three-year-old male fish that may also return to spawn. While still feeding in salt water, the chinook has a dark back, with a greenish blue sheen.
As it approaches fresh water to spawn, its color darkens and it develops a reddish hue around the fins and belly. By the time chinook are typically observed in freshwater, the head is significantly larger than pictured above. Also, spawning males have enlarged teeth and the snout develops a hooked appearance. Some coastal river systems have more than one stock of chinook, sometimes with the stocks migrating in spring or fall.
In the sea, chinook feed on large zooplankton, herring, sand lance and many other fish, ranging widely in the ocean and growing rapidly during their last year in salt water.
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CHUM (Oncorhynchus keta)
Chum salmon are widely dispersed along the Pacific coast from northern California to the Aleutian Islands in the Bering Sea. The distribution of chum salmon in Oregon is generally limited to the lower reaches of large streams and rivers on the north coast. In periods of high abundance they may be found further upstream and occasionally can be observed during coho surveys. While some have been known to weigh up to 35 pounds, chum salmon average between 8 to 14 pounds and measure between 24 and 30 inches in total length.
In shorter coastal streams, young fry move directly to the sea upon emergence from the gravel, sometimes requiring only a day or two for their journey downstream. In the larger river systems, however, the fry may stay in fresh water for several months while making their way to the ocean. They remain in coastal waters until mid- or late- summer before going farther offshore Their growth during this part of their migration is rapid. The young are green-backed, silvery fish with faint parr markings.
In salt water, chum salmon (Oncorhynchus keta) are metallic blue and silver, with occasional black speckling on the back. As they near fresh water on the return to their home streams, their flesh quality and visual appeal deteriorate rapidly. Mature fish show reddish or dark bars across the sides and some have blotches of gray or black as well. Sometimes spawning chum will display a greenish tint, but not as pronounced as in the picture to the left. The males also develop a sharply hooked nose and large, dog-like teeth (hence the common name "dog salmon") which are used to display and protect their territory during spawning.
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COHO (Oncorhynchus kisutch)
Coho salmon (Oncorhynchus kisutch), often called silver salmon, are found in most Oregon coastal streams and in many streams from California to Alaska. Oregon and California coho populations exist at the margins of the overall species range Their major territory lies between Cook Inlet halfway up the Alaska coast, to the Columbia River. While most coho tend to remain close to the coast, they have been found as far as 100 miles inland. When mature in the late fall they average 29.5 inches in length (jacks are less than 17 inches) and weigh up to 25 pounds, although their average weight is between 8 and 14 pounds.
Coho life history patterns revolve around three largely independent age classes, each with a three year generation time. Some breeding interaction between year classes is maintained by the spawning contribution of early returning jacks and the occasional four year old adult. Juvenile coho are highly adaptable and can have varied life histories. Most stay from one to two years in coastal streams before emigrating seaward as smolts. But other fry are equally at home in lakes or in coastal estuaries.
During early stages of growth, they have distinct parr markings (dark, vertical bars along each side), greenish brown backs, and a white leading edge on the anal fin and an orange tint on all but the dorsal fin. As they develop into smolts, their parr marks gradually fade and their backs become green with dark spots.
In the ocean, coho adults, have silvery sides and a metallic blue back with irregular black spots. Spawning males in fresh water may exhibit bright red on their sides and bright green on their back and head, with darker coloration on their belly. They also develop a marked hooked jaw with sharp teeth. Females also change color and develop hooked snouts, but the alteration is less spectacular.
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STEELHEAD (Oncorhynchus mykiss)
Steelhead trout utilize habitat in tidal waters of estuaries and near shore. Adults prey on squid, euphausids, amphipods and fishes; the young eat insects, copepods, amphipods and other crustaceans and young fishes (e.g. sand lance, eulachon, herring). Steelhead predators consist of a variety of fish, birds and marine mammals.
Steelhead spawn in larger streams and rivers. Mature adults enter rivers and larger streams year round, but generally concentrate as winter (November to May) and summer (May to October) runs. Steelhead may spawn more than once (3 to 40 % of the population). Eggs are laid in gravel redds prepared by the female in tributary streams or inlets/outlets of nursery lakes from January to June. Eggs hatch in four to seven weeks and fry emerge from the gravel from mid-June to mid-August. Juveniles rear in freshwater for two to four years prior to migrating to the sea as smolts from April to June, and only remain in an estuary for a short period of time before moving offshore. Adults usually complete extensive feeding migrations in the Pacific Ocean before returning to spawn after two to three summers (range one to four) in the ocean. Adults live six to eight years and may reach up to 45 inches and 42 pounds. 25 to 35 inches and 5 to 20 pounds will be a more typical length and weight range of fish you may see.
Spawning Comparison:
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Fall Chinook: note irregular spots on back Female, Male and Jack Coho
Male, Female and Jack Chinook carcasses Female and Male Chum carcasses
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SPAWNING SURVEY FIELD FORMS
There are four forms used for recording spawning survey data. They are: 1. Spawning Fish Survey Field book (used in field) 2. 2005 Spawner Survey Form (stays in office) 3. Biological Sampling Form 2005 (used in field) 4. Survey Evaluation Form (stays in office)
The function and directions for use of each of these forms is as follows:
Spawning Survey Field Book
• Pocket-sized books with 40 forms per book. • Used for recording survey conditions, tallying fish and redd counts and recording comments (see below). • Data are transcribed to 2005 SPAWNER SURVEY FORM at end of each day. • Completed forms are kept at your workstation and turned in to crew leaders at end of season. • Codes and abbreviations can be found on the front and back cover of the field books.
SPAWNING SURVEY FIELD BOOK:
Survey: ______Date: ______W: ____ F: ____ V: ____ Fish Activity: CH ___ CO ___ CM ___ Live Dead unMk Mk Unk. Jack Male Fem Jack Unk PHA PHJ
Redds (Use reverse side for comments and gravel counts)
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2005 SPAWNER SURVEY FORM
REACH ID:? SEGMENT: SURVEY: DISTRICT: ( )MILE TARGET SPECIES: BASIN: UTM COORDINATES: SUBBASIN: UP-E UP-N DOWN-E DOWN-N SURVEY TYPE:
LOCATION:
R CHINOOK COHO CHUM S Date Surv Survey Live Fish E T eyor Conditions Activity Comments D Live Dead Live DeadLive Dead ID D L mm/dd WF VCH CO CM C1 C2 S AJ MUFJ PHA UnMAMkA UnKA J M F J UAPHA PHJ M F UHD
Send copies of this sheet to the Corvallis Research office on the 1st and 15th of every month. Return original datasheet to Corvallis at the end of the season. 2005 SPAWNER SURVEY DATA FORM INSTRUCTIONS
This data form is used to record tallied counts and activities of spawning salmon and other associated aspects of the survey. • Forms are kept in the office and data are transcribed to this form daily. • Copies of forms must be received by the Corvallis Research Lab (attention: LaNoah Babcock) by the 1st and the 15th of each month for data entry. • Original forms are sent to Corvallis at end of season. • Remember to highlight any changes on both originals and copies
Header
NOTE: Survey location, survey description, survey type and target species are preprinted on forms for all established surveys. All fields in the header will need to be filled in for new survey areas.
Reach ID and Segment: (preprinted on form)
Used to uniquely identify each survey area. Supplied by Corvallis OASIS.
District: (preprinted on form)
1 - North Coast 2 - Tillamook 3 - Lincoln 4 - Siuslaw 5 - Umpqua 6 - Coos/Coquille/Tenmile 7 - Lower Rogue/South Coast 8 - Upper Rogue 20 - Columbia River Management 21 - Lower Willamette
BASIN, SUBBASIN: (preprinted on form)
Major basin and sub basin where survey area is located as defined by Corvallis OASIS.
UTM COORDINATES: (preprinted on form)
UTM coordinates for downstream and upstream boundaries of survey segment.
• Check to see if the coordinates are correct whenever possible. If incorrect, update directly onto spawner survey form and highlight. Make sure to use the Averaging function on your GPS unit when obtaining coordinates.
START COORD: (preprinted on form)
Township, Range and Segment at downstream boundary of survey segment.
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LOCATION: (preprinted on form)
Survey description. Check and revise if necessary. Pay close attention to any instructions for landowner notification/compliance and routes for exiting survey segment.
TARGET SPECIES (preprinted on form)
Species that is the focus of the survey:
1 - Fall Chinook 2 - Coho 3 - Chum 4 - Steelhead 5 - Summer Chinook
SURVEY TYPE (preprinted on form)
1 - Standard index survey 2 - Supplemental survey 3 - Spot-check 4 - Random 5 - Lake (coho only, Tenmile, Siltcoos and Tahkenitch Lakes) 6 - Volunteer 7 - (NWHF) National Wildlife Heritage Foundation 8 - BLM
Body
DATE
Date of the survey: Enter the month and day the survey took place (e.g. 01/22).
SURVEYOR ID
Surveyor ID number
Used to identify the person conducting the survey. If a survey is divided between surveyors, the surveyor filling out the survey form should use his/her ID number. Also make sure when splitting the survey to get ALL of the information from your partner and write it on your survey form.
W (WEATHER)
Describe the weather as:
C - Clear O - Overcast F - Foggy R - Rain S - Snow P - Partly Cloudy
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F (FLOW)
Describe the stream flow as:
L - Low or Dry stream covers less than 50% of the active channel width M - Moderate stream covers 50% to 75% of the active channel width H - High stream width covers > 75% of the active channel width and stream height approaches bankful F - Flooding stream is out of its banks
V (VISIBILITY)
Describe stream visibility as: 1 - Can see bottom of riffles and pools 2 - Can see bottom of riffles 3 - Cannot see bottom of riffles or pools (check several areas before making this determination – see page 56)
LIVE FISH ACTIVITY
Live fish activity of each species observed must be recorded.
13 Most fish spawned out
14 Most fish holding in pools (prior to spawning)
15 Most fish migrating through survey area
16 Most fish actively spawning (as demonstrated by courtship behavior, excavation of redds, competition for mates, and guarding of redds)
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Comments
Use comment codes from the following list. There is room for two comments per survey. Prioritize comments on the Salmon Spawning Survey Form according to the priority of the categories listed below. If further comments would be useful, record the date and comment code on the reverse side of the Spawning Survey Evaluation Form.
Comment Codes
Marks and Tags (Priority I, Highest Priority)
*This category must be represented in the comment section when appropriate*
50 Adipose (CWT) fish observed 51 Adipose (CWT) fish observed, snout recovered 52 Live tagged fish observed 53 Dead tagged fish observed 54 Dead tagged fish observed, tag recovered 55 Fin clipped (other than adipose fin) fish observed
Redds (Priority I, Highest Priority)
71 Number of redds estimated because of high density
Area Surveyed (Priority II Mid Priority)
01 Includes tributary to survey (Used when fish are encountered in tributary of parent survey. See page 57 for details) 02 Holes not surveyed (Used when water is too high to survey holes) 03 Survey boundary description change
Factors Affecting Fish Abundance (Priority II, Mid Priority)
40 Poaching 42 Stream low 43 Stream dry 44 Instream habitat improvement in or near survey section 45 Habitat damage in or near survey section 46 Passage barriers below survey area 47 No survey conducted due to drought conditions 66 Actual number probably substantially higher than observed 97 Placed coho carcasses
Viewing Conditions (Priority II, Mid Priority)
20 Dark (pertains to the light source, not the water clarity) 21 Dark in pools (pertains to water quality, often tannins) 22 High glare 23 Partly frozen 24 Not surveyable (stream too high and/or turbid, counts will be disqualified)
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Comments (continued)
Survey Timing (pertains to TARGET SPECIES) (Priority III, Lowest Priority)
NOTE: These codes need only be used when two or more surveys during the season are separated by more than ten days. These codes are used in cases where the stream segment is not surveyed over the course of the spawning season (typically due to extreme stream flows). They are an indication of whether the surveyor feels the peak run was sampled or the survey was ended too early or too late.
10 Peak survey 11 Survey too early--before peak 12 Survey too late--after peak
Stream Conditions within the Survey Area (Priority III, Lowest Priority)
31 Impassable logjam 32 Passable logjam 33 Impassable beaver dam 34 Passable beaver dam 35 Impassable culvert 36 Evidence of scouring of streambed 37 Severe stream bank erosion 38 Passable culvert
Miscellaneous (Priority III, Lowest Priority)
60 Most carcasses washed out 67 No new spawning fish observed 61 Heavy silt deposition in streambed 88 Road closed or impassable/ 62 Count in holes estimated inaccessible 64 Exposed redds due to low flow 39 Octopus at milepost 12 65 Redds obliterated due to high flow
REDDS
Number of spawning redds observed
A redd is defined as the single excavated depression dug by a female. Individual redds may overlap,. and form clusters. A redd may be identified by a hollow in the gravel and the adjacent downstream plume of excavated gravel. The gravel from a recently dug redd will usually appear lighter colored and less uniformly oriented than the undisturbed gravel. Care should be taken not to confuse redds with general stream scouring or scouring associated with wood, rootwads, or larger rocks.
When it is not possible to distinguish individual redds because of high redd density estimate count and include comment 71 under comments.
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CHINOOK
LIVE
A -Number of live adults J -Number of live jacks
DEAD
M -Number of dead males F -Number of dead females J -Number of dead jacks U -Number of dead unknown sex PHA -Number of previously handled dead adults (tails removed)
A chinook jack is defined as a male measuring 510 mm (20 inches) or less in MEPS length or 600 mm (24 inches) or less in fork length.
MEPS length is the "mid-eye to posterior most scale" (anterior edge of tail) measurement.
COHO
LIVE
UnMA -Number of live adults with intact adipose fin MkA -Number of live adults with adipose fin removed UnKA -Number of live adults, presence of adipose fin undetermined J -Number of live jacks
DEAD
M -Number of dead males F -Number of dead females J -Number of dead jacks U -Number of dead unknown sex or unknown finclip PHA -Number of previously handled dead adults (tails removed) PHJ -Number of previously handled dead jacks (tails removed)
A coho jack is defined as a male measuring 430 mm (17 inches) or less in MEPS length, or 500 mm (20 inches) or less in fork length.
CHUM
LIVE
A -Number of live adults
DEAD
M -Number of dead males F -Number of dead females U -Number of dead unknown sex
STLHD Number of steelhead (total count of live and dead).
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Biological Sampling Form Surveyor ID______Year______Page ___ of ___
Length (MEPS) Mark-Recapture Opercule Condition Segment Carcass
Species coho and/or chinook chinook Line # Clip Date Reach ID Sex Scale # DNA # Snout # only Comments Color Left Right
Carcass Carcass mm/dd Tagged Tag Recov.
Tag 1 Tag 2 C1 C2 C3 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 BIOLOGICAL SAMPLING FORM (BSF) INSTRUCTIONS
This form is to be completed for all carcasses that are sampled for biological data
• If a Fish carcass is to be scale sampled, Coded-wire tag (CWT) sampled, DNA sampled or examined for marks or tags tally the fish under the appropriate heading on the Spawning Survey Field Book, then complete both this form and the scale envelope.
• Take this form in the field and always fill this form out at the time of sampling.
1. The Biological Sampling Form is in a booklet format. Abbreviated form instructions are located on the inside and back cover. To enter data, open the booklet to the center page and complete the required fields. When a page is completed, pull it from the booklet, and place the page in the prescribed notebook, which should be kept in the survey vehicle at all times.
2. Be very organized about the use of this form. If a page is nearly complete, and the next survey is expected to have a large number of samples, file the current page in the notebook and start the survey with a fresh page. Otherwise, multiple surveys and/or days can be placed on the same page.
3. ALWAYS write your surveyor ID # in the prescribed location (top left of page). Never share a page of this form with another surveyor.
4. Live counts of coho in the Smith and NF Nehalem River Basins should be tallied on the form provided on the backside of each Biological Sampling Form.
5. Codes for each of the fields are included inside the front and back covers. Use only the codes prescribed, or face severe punishment from the data-entry Goddess.
6. Copies of the first two weeks of scale sample data are to be sent into the Corvallis Research Lab (attn: LaNoah Babcock). Thereafter the original form is to be sent into the office upon completion of each page.
7. This form will be taken on all surveys, and a line from this form will be completed for each carcass sampled. Remember, all coho carcasses will be scale sampled, which means for every coho carcass found, a line in the Salmon Carcass Biological Sampling Form should be completed. Consult crew leaders for other species sampling quotas.
8. Do not take samples from placed carcasses (crew chiefs should know if carcasses have been placed.)
BSF Header Surveyor ID
Unique code for each individual surveyor found on page 6. One surveyor per form page. This field MUST be completed.
Year
Complete this field by recording the year of the survey season. The year to be recorded is 2005, even if the sample was taken in January of 2006.
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Page___of___
Pages should be numbered in series (1,2,3 …) only if data is continuous from a single survey.
BSF Body
Note: Mandatory fields must be completed for all carcasses sampled.
Line #
(Pre Labeled) Each page has 25 line numbers. Each line represents a single sampled carcass.
Date ( Mandatory)
Date of the sample. Enter the month and day the sampling takes place.
Reach ID and Segment ( Mandatory)
Used for uniquely identifying each survey area. Consult the Survey description list prior to each survey.
Species (Mandatory)
Use only these codes:
Species Codes 0=Unknown 1=Chinook 2=Coho 3=Chum 4=Steelhead
Sex Codes (Mandatory)
1=male 2=female 3=unknown
Length (Mandatory)
MEPS length measured in MM.
Clip (Mandatory)
This field captures data on three fin clips; the adipose fin and the left and right ventral fins (multiple clip codes should be separated by commas). Remember that adipose clipped fish must have their snouts removed and placed in a plastic bag with a snout ID label. See page 22 for fin locations.
USE ONLY THESE CODES!
Fin-Clip Codes:
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2= Adipose fin clip 4= Left Ventral fin clip 5= Right Ventral fin clip 6= Left Maxillary clip 7= Right Maxillary clip 0= No fin clips Enter for all carcasses having no fin clips. 99 = Clip status is unknown (scavaging, etc.)
Carcass Condition
Complete this field for all DNA sampled coho and chinook. This field is intended to elucidate the time since death of the fish. 1 = Fresh carcass, firmer flesh, little odor, recently deceased. 2 = Aged carcass, increased decomposition and maloderous 3 = Severely decomposed carcass. Pudding.
Scale # ( Mandatory)
Unique number printed on scale envelope. Write number found on scale envelope in this field. See page 46.
DNA # Taken for coho and chinook in selected basins.
Complete this field using the unique ID # printed on the DNA vial. If carcass is clipped leave this field blank. See page 49 for sampling instructions
Snout # Adipose clipped fish of all species only
Complete the snout # field by inserting the entire number found on the snout ID label. (Example 05H 9999). Remember that all carcasses with adipose clips will have the snouts removed, and that all snouts receive their own uniquely numbered snout ID label. The label itself is placed with the snout inside the plastic snout bag. If the carcass is not adipose clipped then leave this field blank. NOTE: If a snout wand was used and no tag was detected, put a dash in the Snout # column, and in comments write in code 56 (wand used) and code 96 (no snout taken).
Mark Recapture Study Sites (Siletz chinook and Siuslaw chinook and coho only).
This section of the Biological Sampling Form has three columns, all shaded in light gray. They are labeled as Color, Carcass Tagged or Tag 1, and Carcass Tag Recovered or Tag 2. It is important to note that the two separate columns (Carcass Tagged or Tag 1) and (Carcass Tag Recovered or Tag 2) actually represent two different fields each. It is not as confusing as it sounds, since the “Carcass Tagged” and “Carcass Tag Recovered” fields are to be used by the Chinook Research and Monitoring Project surveyors only, and will not apply to OASIS personnel (that is you).
The sections of the Mark-Recapture columns that are relevant are the ”Color”, “Tag 1” and “Tag 2” fields.
Color This field captures the color of the tag found on the carcass. The tags will be thin spaghetti-shaped, colored pieces of plastic implanted into the body of the fish just beneath the
42 dorsal fin. All tagged fish received two tags of like color at the time of their trapping. Color codes are found below.
Color Codes
B=blue R= Red Y=Yellow O=Orange G=Grey or Brown
For Smith River and NF Nehalem Tags in the Smith and NF Nehalem are labeled with numbers. For each tag found, write the tag # under “Tag1” and/or “Tag 2”. Use dashes under Tag 2 if only one tag is found. Leave all three fields blank if no tags found. Examples are below. Nehalem Smith One Tag: Mark-Recapture Mark-Recapture
Color Carcass Carcass Tag Color Carcass Carcass Tag Tagged Recov. Tagged Recov.
Or Tag 1 Or Tag 2 Or Tag 1 Or Tag 2 O 1 ______G 9998 ______
Two Tags:
Mark-Recapture Mark-Recapture
Color Carcass Carcass Tag Color Carcass Carcass Tag Tagged Recov. Tagged Recov.
Or Tag 1 Or Tag 2 Or Tag 1 Or Tag 2 R 1 1 B 9998 9916
Opercule (All Chinook sampled in the Siletz and all Coho and Chinook in the Siuslaw.)
Opercule (or gill cover) punches. Opercule punches are circular holes cut in the Operculum, which is the bony flap covering the gills on both sides of the fish’s head. Punches may occur on the left operculum, the right operculum or both. For each side there are three possible punch locations: Above center, below center, and center. These punches are to be found on chinook in the Siletz, and both Chinook and coho in the siuslaw. One fish may have punches on both operculum.
Opercule Punch Codes: (Fill out for both left and right operculum)
A=Above Center B=Below Center C=Center D=Double (any combination of punches/per side) U=Unknown N=No Mark
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Comments Use codes listed below
41=Scavenging 95=Tagging Mortality 90= Prespawn 96=No Snout Taken 92=No Scales Taken 55=Fin clipped (other than adipose) 93=Seal Marks 56=Snout wand used 94=Net Marks
Live Counts - Smith River and NF Nehalem basins
In the Smith River and North Fork Nehalem basins special tallying categories for observations of live coho exist. The form located on the backside of each individual page of the Biological Sampling Form should be used for live counts of coho in these basins. Crews outside of these two basins will not use this portion of the form. • Multiple surveys can be represented by drawing lines between each survey’s data. • Surveys being tallied on this form should relate to the surveys represented on the same piece of paper on the Biological Sampling Form.
ADULT LIVE COUNTS Seg.
Date Reach Tag Tag Tag No Tag No tag Unknown Smith and NF Nehalem ID Color 1 Color 2 Color 3 Ad-Clip mm/dd ______
Live Counts
JACK LIVE COUNTS
Date Reach Seg. Tag Tag Tag No Tag No tag Unknown ID Color 1 Color 2 Color 3 Ad-Clip mm/dd ______
Date, Reach ID, Segment Record date, Reach ID and segment as per Bio Sampling page. Multiple surveys may be represented by drawing lines to separate each surveys data.
Tag color 1, 2 and 3 For the three “tag color” columns write in the tag colors you observe on live coho under either tag 1, 2 or 3, then tally the number of fish observed of each. For example, if two live coho were observed with a red tag, and one coho was observed with a blue tag the correct tally would be:
Tag Color Tag Color Tag Color 1 2 3 _Red_ _Blue______II I No tag If no tag observed on live coho tally under “No Tag”. No tag Ad-clip If no tag observed on coho with an adipose clip, then tally under “No tag Ad-clip.” Unknown If tags and clips are unknown for a live observed coho, tally under “ Unknown.”
44
CODED WIRE TAG AND FIN-MARK RECOVERIES
Instructions
Recovery of Coded Wire Tags (CWT’s) and fin marks from salmon encountered on spawning fish surveys are used to assess straying of hatchery salmon to natural spawning areas. CWT's are uniquely marked minute pieces of wire that are inserted into the fleshy part of a salmon snout prior to being released from hatcheries. These tags are a primary method for identifying groups of salmon released from hatcheries. CWT salmon are recognized by the absence of their adipose fin that is cut off at the time of tagging. CWT recoveries are decoded by removing the snout from adipose-clipped fish and sending the snout to the CWT processing lab for dissection and reading. In addition to CWT's, adipose fin clips and other fin marks are used to identify hatchery salmon. The occurrence of these fin marks are also recorded from salmon carcasses recovered on spawning surveys. The following procedures are used to sample CWT and fin marked salmon and record recovery data:
1. Carry Snout ID Labels with you at all times while surveying.
2. When a fin-marked carcass is found, tally the fish under the correct heading in the field book. Then complete one line for each fin-marked carcass in the Biological Sampling Form, completing all applicable fields, and noting the apropriate code for the corresponding fin-clip.
3. Instructions for Adipose clipped fish. If the fish has a clipped adipose fin, remove the snout from behind the eyes to the tip of the jaw and place in a plastic snout bag with a snout ID label (page 46). Complete all applicable fields on the Biological Sampling Form. Write the snout ID label number on Biological Sampling Form in the Snout # Column. Snout samples are needed for all adipose fin-clipped fish.
4. Use of Snout Wands (Lower Columbia Crews Only) In areas with heavy hatchery influence and large numbers of carcasses, a snout wand may be used to detect CWT’s and reduce sampling effort. Consult crew leader prior to use.
When adipose clipped fish are encountered and a snout wand is available, complete all applicable fields on the Biological Sampling Form and use clip code “2” (Adipose clipped) in the clip column.
• If a CWT is detected, remove the snout and place in a plastic bag with snout ID label. Record the snout ID label number in the Snout # Column on the Biological Sampling Form. Use the comment code 56 (snout wand used) in the comments column.
• If no CWT is detected do not remove the snout and use comment code 56 (snout wand used) and 96 (no snout taken). Put a dash in the Snout # column of the Biological Sampling Form.
Snout wands should be tested at the beginning of the season and at least once a week throughout the season. Consult your crew chief about proper snout wand technique and maintenance.
5. At the end of the season, snouts will be picked up from the field offices and transported to Clackamas for processing. Attach a label to the container of snouts that shows (1) the area of origin, (2) the year, and (3) a statement that they were recovered on spawning fish surveys.
45
All carcasses must be examined for fin marks! Fin-marked carcasses are recorded on the Biological Sampling Form and snouts are collected from all adipose-clipped carcasses.
2005 SNOUT ID LABELS
NUMBER SERIES CREW LOCATION 05H 7700-7749 SANDY 05H 7750-7774 SAUVIE’S ISLAND 05H 7500-7550,7775-7799 ASTORIA 05H 7800-7899 CLACKAMAS 05H 7200-7299 SEASIDE 05H 7300-7349 JEWELL 05H 9300-9400 NORTH FORK NEHALEM 05H 7400-7499 TILLAMOOK 05H 8000-8024 CORVALLIS 05H 7350-7399 NEWPORT 05H 8025-8049 MAPLETON 05H 8050-8099 EUGENE 05H 8100-8124 ROSEBURG 05H 8200-8299 REEDSPORT 05H 8300-8399 COOS BAY 05H 8125-8174 SMITH RIVER FALLS CREW 05H 8175-8199 BRUCE MILLER’S CREW 05H 8400-8459 GOLD BEACH 05H 8460-8499 GRANTS PASS 05H 8660-8699 Mark Stone/ Kip Woods 05H 8750-8799 Steve Johnson and Crew 05H 8725-8749 Lincoln District Volunteers 05H 7551-7699 NORTH COAST-- 05H 7000-7199 SPRING CHINOOK
EXAMPLE OF SNOUT ID LABEL (actual size)
05H 9999
46
SCALE SAMPLING
Scale samples taken from salmon carcasses encountered on spawning fish surveys are used to assess age composition, hatchery-wild ratios, and growth rates of salmon populations. Growth is recorded on scales in rings or circuli, not unlike those found on trees. When mounted and projected these circuli patterns can be read to reveal the life history of each fish sampled, including amount of time spent rearing in streams, time of ocean entry, and the number of years spent in the ocean. This information ultimately is used to aid in forecasting stock abundance and in assessing fishery harvest impacts.
Once a carcass has been sampled its tail should be cut off. Any carcass found without an intact skeleton (precluding a MEPS measurement) should not be sampled, but instead recorded in field book as “Previously Handled”.
Sampler 007 Date 11/25/03 00001 Example of a Scale Envelope with data Species:_____02____ Basin____Siuslaw____ fields completed Reach__22504.00______Seg___2______
Comments:
OREGON DEPT. OF FISH AND WILDLIFE
Filling Out Scale Envelope
All scale card fields must be completed as follows:
Sampler Enter the surveyor ID number of the individual who is sampling the scales. This surveyor ID number must match the surveyor ID of the individual filling out the Biological Sampling Form.
Date Enter month, day, and year
Scale Number Scale number. Each scale card is uniquely numbered. This number must be entered on the Biological Sampling Form under scale #.
47 Species For each species use the following codes: Species Codes 0=Unknown 1=Chinook 2=Coho 3=Chum 4=Steelhead
Basin Provide the name of the Basin (found on the spawning survey list)
Reach Provide the reach ID (found on the spawning survey list) of the survey the scales were sampled from. Include two decimal places.
Segment Write the survey segment number the scales were sampled from.
Comments Write comments using words or codes found on inside cover of Biological Sampling Form.
Scale Sampling Instructions Coho Salmon
1. Sample scales from all carcasses found (excluding placed carcasses).
2. Cut-off tail from all fish that are scale sampled to avoid re-sampling.
Chinook Salmon
1. Sample all carcasses from the following index basins Siletz Siuslaw
2. Sample 200 chinook in each of the six following Index Basins: Nehalem Wilson Salmon Coquille Sixes Chetco
3. Sample scales from all fin-marked chinook.
4. Cut-off tail from all fish that are scale sampled to avoid re-sampling.
48 Chum Salmon
1. Collect scale samples from 250 chum salmon from each of the following basins: Nehalem, Tillamook Bay and Yaquina.
2. Cut-off tail from all fish that are scale sampled to avoid re-sampling.
Scale Sampling Procedure
This procedure should be followed when sampling scales from any salmon or steelhead.
1. Locate key area by following the diagonal row of scales down and back from the posterior insertion of the dorsal fin to the first 3 scales above, but not including the lateral line. One to two scales in front of (anterior) and behind (posterior) these three scales are within the key area.
2. Scrape the key area with a knife to remove any slime. With forceps, pluck 4-5 scales from this area and place them neatly between the paper insert in the envelope. Be very careful that the scales come from the key area.
3. Turn fish over and repeat procedure on the other side of the fish, placing scales in the same envelope.
4. Write any pertinent information regarding that fish on the envelope.
5. If scales are absent from the key area on one side of the fish, sample from the key area on the other side of the fish. If scales are absent from key areas on both sides of fish, do not take scales, but complete Salmon Carcass Biological Sampling Form, writing code 92 (no scales taken) under comments.
49 6. Pull the paper sleeve 2/3 of the way out of the scale envelope, then fold the upper half backward over the top of the envelope when placing scales inside the sleeve. Do not stack the scales. Taking the sleeve completely out of the envelope not only takes more time, but also causes wrinkling of the scales and can render them (and you) useless.
7. Keep all the scale samples organized and in the same place – scales should be stored in a dry location with adequate ventilation. Tupperware containers with perforated lids are provided for daily deposition of samples, and a larger box located in a safe location is excellent for longer-term storage. Placing scales in Ziploc bags or other sealed environments causes scales to decompose. This in turn makes your rig, office, or pants smell like dead salmon and you generally less popular with other, less odiferous, human beings. Yum.
DNA SAMPLING
Background
Samples of DNA taken from Salmon Carcasses are used to map the genetic variance represented within coastal coho and Chinook populations. This information will be used in turn to determine which components of the variation in life history are critical for long term viability of this species. In effect, DNA sampling is the first step in an effort to understand the various genetic recipes for success in coastal populations. We will be taking chinook DNA samples in selected coastal basins and coho DNA in hatchery fish on the NF Nehalem and S. Umpqua River basins.
Instructions
Each surveyor will be issued a small tray containing 96 sample vials arranged in a grid pattern. Before going in the field take an adequate selection of these vials and place them in a safe container (Ziploc or Tupperware). Insure that you never run out of vials while in the field by leaving extra empty vials in your vehicle. If you have nearly completed a tray contact your crew leader to obtain another.
Chinook will be sampled in the Sixes, Coos, Milicoma, Yaquina, Nestucca (at Cedar Cr. Hatchery), Necanicum, Trask, Kilchis, and Wilson basins this season. Other than coho DNA sampling of hatchery fish in the NF Nehalem and South Umpqua, coho will not be sampled in 2005. To sample DNA cut a segment of the flesh from any fin (the harder ray material is not the target) with a pair of scissors and place fleshy material in an individual DNA vial, record the last five digits of the number found on the DNA vial onto the Biological Sampling Form under the DNA # field, then place the vial in a safe container reserved for DNA samples. At the end of the day place the day’s DNA samples back in the rack the vials came in. Please do your best to rack the vials according to numerical order. The goal isn’t to fill the vial completely with a fin sample. This will only make preserving the sample more difficult. Instead, cut off a sample that doesn’t exceed 25% of the total volume of the vial. Extremely decomposed carcasses should be skipped since it is difficult to amplify DNA from these fish (i.e., if the sample is soupy, it probably won’t amplify).
50 SPAWNING SURVEY EVALUATION FORM 2005
REACH ID SEGMENT # SURVEY NAME
ID # OF SURVEYOR COMPLETING FORM DATE OF FORM COMPLETION
PROBLEMS WITH SURVEYING THIS STREAM SEGMENT: ______
BARRIERS TO UPSTREAM MIGRATION:
APPROX. DID IT BECOME WERE SALMON LOCATION NATURE OF BARRIER PASSABLE? WHEN OBSERVED (0.1 MILE) (DATE)? UPSTREAM FROM IT
ESTIMATES OF SPAWNING GRAVEL QUANTITY:
SURVEYOR ID DATE SPAWNING GRAVEL (M2)
DISTRIBUTION OF SPAWNING GRAVEL (% OF TOTAL):
DOWN- LOCATION WITHIN SURVEY SEGMENT UP- STREAM START TO 1/4 1/4 TO 1/2 1/2 TO 3/4 3/4 TO END STREAM BOUNDARY BOUNDARY
DISTRIBUTION OF SPAWNING FISH (% OF TOTAL):
DOWN- LOCATION WITHIN SURVEY SEGMENT UP- STREAM START TO 1/4 1/4 TO 1/2 1/2 TO 3/4 3/4 TO END STREAM BOUNDARY BOUNDARY FISH DISTRIBUTION BASED ON: FISH REDDS (CIRCLE ONE)
HABITAT RANKING (circle): NO HABITAT VERY POOR POOR OK GOOD VERY GOOD EXCELLENT
GENERAL COMMENTS AND ADDITIONAL CODED COMMENTS (USE REVERSE SIDE)
51 INSTRUCTIONS: SALMON SPAWNING SURVEY EVALUATION FORM
This form is used to evaluate the spawning habitat for coho salmon in a given survey segment throughout the spawning season. It is also used to note any factors that may influence our ability to obtain accurate estimates of spawner abundance in the survey segment. One form is to be completed for each coho survey segment. Notes can be written on the Spawner Survey Form as the season progresses.
REACH ID Enter 7-digit survey identification code (i.e. 25680.50).
SEGMENT # Enter 1 digit segment identification code.
SURVEY NAME Enter name of survey (i.e. Salmon Creek).
SURVEYOR ID Enter the surveyor identification code of the surveyor who is completing the form.
DATE OF FORM COMPLETION Enter date on which form was completed.
PROBLEMS WITH SURVEYING THIS STREAM SEGMENT List any major problems that prevented the survey from being made or caused the survey to be difficult (road conditions, extended high stream flows and/or turbidity, problems with access through private land, etc.). Identify any factors related to the condition of the survey segment that may have hindered your ability to make accurate counts of salmon (water clarity, structure in the stream channel, viewing conditions, etc.).
BARRIERS TO UPSTREAM MIGRATION List up to three potential barriers to upstream migration occurring within the survey segment during the course of the spawning season. Wait until the first freshet (high water) has occurred before identifying barriers. Barriers are best identified by the presence of salmon immediately downstream from an obstacle but not upstream of the obstacle. Record the approximate location of the barrier from the survey starting point (nearest 0.1 miles from the start), nature of the barrier (e.g., beaver dam, culvert, log jam, waterfall, etc.), and the date when the barrier became passable (date when fish were first observed upstream from the barrier or when high flows removed the barrier). If you feel the barrier prevented fish passage for the entire season, note as such. If the endpoint of the survey is a barrier, mention that too.
ESTIMATES OF SPAWNING GRAVEL QUANTITY After the first freshet, you will estimate the quantity of gravel in each quarter of your Coho surveys once every month (total of three counts - See page 53 for method of gravel measurement). It should be possible to estimate the quantity of spawning gravel while doing the survey without spending a lot of extra time. If hand tally counters are available, they may be helpful. Write estimates on the Spawner Survey Form in the right margin by the date the estimate was made to keep track of when the last gravel counts were done.
52 DISTRIBUTION OF SPAWNING GRAVEL Estimate the proportion of spawning gravel in each quarter of the survey to the nearest 5%.
DISTRIBUTION OF SPAWNING FISH Estimate the proportion of spawning fish in each quarter of the survey to the nearest 5%. Remember to indicate whether fish or redds were used to make the estimate.
GENERAL COMMENTS Use the reverse side of the Spawner Survey Form as the season progresses to record observations that will help you complete this form. List any comments that may help us in interpreting your responses, and list any other noteworthy features of the survey segment. Some possible questions to consider include: What are your impressions of the habitat? Did the habitat significantly change during the season, and if so, how? Are spawning habitat improvement structures present, and are they functioning to improve spawning habitat? If no coho were seen, do you have any idea why? Were there any tributaries within the segment where coho were seen holding at the confluence? Were the names, addresses, and/or phone numbers of landowners mentioned in the description correct? Was this survey unusual compared to other surveys you have done? In what ways?
In many cases you will see certain sections of a stream more than any person on the planet. You may end up learning things about a stream that no one else knows. If you feel that you have information that would increase the quality of our data, correct possible errors in our stream database, or improve our understanding of a certain stream, this form is where that information should go.
DESCRIPTION OF COHO SALMON SPAWNING GRAVEL
Suitable spawning sites for coho salmon are characterized by gravel size, water depth, and water velocity. Preferred sites for redds are located at the tail end of pools or the head end of riffles (tail-outs), however other habitat types such as glides or side channels may also be used. Tail-outs appear to be preferred because they offer (1) large uniform gravel deposits, (2) a gradient of water depth and velocity, allowing options for redd construction over varying stream flow, (3) good inter-gravel flow through down-welling of stream flow and (4) protection from gravel scouring during freshets. Following is a listing of the physical parameters of optimal redd sites of coho salmon in Oregon coastal streams:
Habitat Unit Type • Pool tail-out
Gravel Size • < 15 cm (6 in) in diameter • > 2 cm (0.5 in) in diameter • Prefer mean diameter of 9 cm (3-4 in) • < 50 % of gravel area intermixed with fines (mud, silt, sand) or with larger rock (cobble, boulder)
Volume of Gravel Patch • > 20 cm (8 in) depth of deposit (thickness) • > 2 M2 (36 ft2) surface area of deposit
Water Depth Over Gravel • < 62 cm (24 in) • > 4 cm (2 in) Prefer mean of 18 cm (7 in)
53 METHOD OF ESTIMATION OF COHO SPAWNING GRAVEL DURING SPAWNING SEASON
The availability of spawning sites (quantity of spawning gravel) can be estimated during spawning surveys by quantifying the occurrence of suitable gravel deposits within the stream channel under baseline winter flow conditions. If spawning is observed in habitat other than optimal habitat, record those observations in the Spawning Survey Evaluation Form.
Follow this procedure when conducting spawning gravel estimates:
• Within the wetted channel width under low or moderate flows, count each two- square meter (2 M2) patch of gravel that is between 4 cm (ankle height) and 62 cm (knee height) below the surface of the water. Gravel size can range from that of a marble to that of a grapefruit, but should average about the size of a baseball. No more than 50% of a patch should consist of fines (sand, silt, mud) or large rock (cobble over 6 inches in diameter or boulders). Do not count thin layers of gravel over silt or bedrock; you should be able to bury your foot in the gravel.
• Gravel deposits larger than 2 M2 are counted by estimating their area to the nearest M2 and adding this value to your tally. Gravel patches should be relatively level, located in the tail-out of a pool, and not piled up at a steep angle against the bank. If the water velocity over the gravel is excessively fast, the gravel will not likely be used. Make the first estimate after the first freshet, and make one estimate per stream per month starting in November.
54 GENERAL SURVEY INSTRUCTIONS
1. Submit copies of the Spawner Survey Forms to the Corvallis office (attn: LaNoah Babcock). Copies must be received by the 1st and 15th of each month.
2. Submit copies of the first two weeks of data from the Biological Sampling Forms. Thereafter, send in the original once each sheet is completed.
3. For survey areas where Area-Under-the-Curve (AUC) estimates are made (all standard surveys and any coho surveys), intervals between successive counts cannot exceed 10 days from the date when the first visit is made.
4. Surveys made under water visibility rating 3, or surveys having the comment not surveyable are not counted when calculating this interval.
5. Examine all carcasses for fin clips and tags, and remove snouts from all adipose clipped fish. Record all fin-marked carcasses on Salmon Carcass Biological Sampling Form.
6. Remove tails from all coho carcasses after examining for fin clips and all other salmon carcasses that are scale sampled or examined tag recoveries (mark-recapture basins).
7. Leave dead fish where they are found.
8. Only count carcasses with intact skeleton (skull through caudal peduncle). For coho and chinook, fragmented skeletons must be tallied under “pre-handled” on SPAWNER SURVEY FORM.
9. Use polarized sunglasses. Yellow or amber tinted lenses are best. Saliva or spray-on defogger may help reduce condensation on the glasses.
10. Walk all stream channels (side channels, backwater pools, etc.).
11. Keep the direction of the survey consistent throughout the season.
12. Wait until the end or termination of the survey to classify weather, flow and visibility for each survey area. Comments should reflect the conditions of a majority of the survey.
13. Ensure that each survey description is clear and accurate, and that survey starting and ending markers are intact. If necessary, revise the survey description using the SPAWNING SURVEY LOCATION DESCRIPTION FORM and replace the markers. Fill out forms or take excellent notes the day the changes are made to avoid forgotten details.
14. If the mileage of a survey area is revised or changed, submit a new SPAWNING SURVEY LOCATION DESCRIPTION FORM.
15. Need GPS coordinates for start and end points whenever UTM's are missing, and for sites that were last surveyed prior to 2000. Update this information on the SPAWNER SURVEY FORMS.
16. Count all species of salmon and steelhead seen in each survey area regardless of the target species of that survey area.
17. If live fish of any species are observed during a survey, note whether most are (A) holding in pools, (B) migrating through survey area, (C) actively spawning, or (D) spawned out. Use codes13-16 to record this on the SPAWNER SURVEY FORM. These data are mandatory anytime live fish of any species are observed.
18. Record survey data in the SPAWNING FISH SURVEY FIELD BOOK AND SALMON CARCASS BIOLOGICAL SAMPLING FORM, and transfer the data to the SPAWNING FISH SURVEY FORM as soon as possible. Carefully read the instructions for completing the forms at the beginning of and throughout the season.
55 Sanitizing Snorkeling Gear to Reduce Spread of Invasive Aquatic Biota- ODFW/Oregon Adult Salmonid Inventory and Sampling Project
Background: New Zealand Mud Snails (NZMS) and other invasive biota can spread rapidly among water bodies in the western United States. Dispersal of NZMS is restricted to transport in water or damp media (Hosea and Finlayson 2005), and it is thought that recreational anglers and other water enthusiasts are primary vectors for dispersal. Traits that promote rapid colonization of NZMS include small size (max length ~6 mm), resistance to desiccation (50% survival post 25 days on damp media; Winterbourn 1970), and the ability to reproduce through parthenogenesis (female production of offspring without fertilization). OASIS site selection is randomized across stream reaches in Western Oregon and the Lower Columbia, and because crews wade in multiple streams throughout the field season, it is important we reduce the dispersal threat of NZMS and other invasives by removing them from our gear.
Reducing Mudsnail Transport Between Basins: Whenever possible, OASIS crews can minimize accidental mudsnail transport across river basins by not sampling in more than one major basin per day. Crews should sanitize field gear daily when they return to their duty station, or between sites if they must sample in major basins in one day. For purposes here we’ll define major basins at the 4th Field HUC level (see maps in sample packets). The following chemical protocol to sanitize gear was developed for crews visiting more than one basin per day*. The protocol is based on research that showed that 100% of snails were killed in 5 minutes with a 1000 ppm concentration of Copper Sulfate (Hosea and Finlayson 2005). The chemical procedure and materials can be adapted by other crews that have nets and other collection gear.
Equipment to be kept in vehicles for site to site sanitation within a day: • one or two 5-gallon plastic water jugs, filled with fresh tap water • Spray bottle w/ copper sulfate solution (might need 2-3, depending on number of crew) • soft bristle brush • spray-rinse apparatus: pressurized hand pump sprayer (1-3 liter) • drip tote • MSDS for Copper Sulfate
Equipment to be stored at duty station • one 7-gallon plastic jug for Copper Sulfate stock solution (see stock dilution below)**
1) Wash/remove mud and large debris from all gear exposed to stream water. (This can be done as a last step before leaving the creek). At vehicle, remove gear and remove insoles from wading boots 2) Put gear in drip totes and hand-spray with cleaning solution to point of saturation and runoff. Gently scrub boot grommets, felt soles and wader folds to remove hidden snails. Clamp top of waders closed to avoid getting copper sultfate on inside where it could come in contact with skin. Allow treated gear to sit for a minimum of 5 minutes 3) Rinse gear with clean water provided in plastic water jugs. DO NOT USE STREAM WATER. Fill pump sprayer with tap water and use it to rinse gear sufficiently. For crews that can return to the duty station a good source of rinse water are outdoor hoses at ODFW offices.
* If temperature and desiccation treatments can be used between site visits (see protocol developed by Aquatic and Riparian Effectiveness Monitoring Program-AREMP, [email protected]), care should be taken so that neck, wrist, and foot seals of Dry-suits are not damaged.
**Field crews will be given pre-weighed packets of 26.5 g Copper Sulfate to make a 7 gallon stock solution of sufficient strength of the active ingredient (252 mg/l Cu). Use latex gloves to handle copper sulfate and avoid contact with skin. Clearly mark the stock solution container and store in a safe place. Refer to the MSDS sheet for more information.
For photos and more information on mud snails, and maps of documented distributions, go to: http://www.esg.montana.edu/aim/mollusca/nzms/
Literature Cited: Hosea, R. C. and B. Finlayson. 2005. Controlling the spread of New Zealand Mudsnails on wading gear. California Department of Fish and Game Administrative Report 2005-02.
Winterbourn, M. 1970. The New Zealand species of Potamopyrgus (Gastorpoda: Hydrobiidae). Malacologia 10:283-321. FIRST WEEK PRIORITIES
1. Meet with crew chief and district staff to go over and/or devise a safety check-in procedure. Field stations will need to have a check in/out board or system in place that will let others know where you are going and when and if you have returned. Isolated crews will need to devise a call in system with their crew chief.
2. Office review with crew chief: Go over all forms and procedures. Review entire manual. Determine snout and scale card storage and any other office protocols.
3. Field review with crew chief: Try to go to a survey that will have fish. Go over survey technique, fish and redd identification, gravel counts, and carcass processing. Each crew can plan on conducting the first few surveys together if they wish to.
4. Sit down with crew chief and identify early season priority surveys. These should include all standard Chinook surveys and any coho surveys that have a history of early returns. It is vital that these surveys be started at the earliest possible date.
5. Go over each survey description and landowner sheet. Mark all sites on a map. Draw up a likely survey rotation. Plan on doing an average of six to eight sites a day.
6. Contact landowners that still need to be contacted. Start with landowners on the priority survey list. Use the county website and courthouse to identify unknown properties. Consult with crew chief on landowner contact techniques if need be.
7. Some crews may need to shuttle vehicles from Corvallis. Once you have your vehicle, check to make sure that you have a working jack, lug wrench, and inflated spare. Vehicles should also have chains and a first aid kit. Make a copy of the key (when needed) and attach it to a concealed location on the rig. You may want to leave a flashlight in the rig as well. Note the mileage of the next needed oil change/service.
8. Contact private timber companies and government agencies and obtain all needed gate keys. Survey descriptions should note if a key is needed. In a few cases, ODFW district offices will have keys that you might be able to use.
9. It may be helpful to make up two spreadsheets. One for survey dates and counts, and another for early season survey status. The dates and counts spreadsheet will be very helpful as a quick reference update, and for planning.
56
Dealing with Special Circumstances
• MISSING SURVEY PARTNER:
What should you do if your partner does not return from a survey? Partners will survey separately unless specifically noted in the directions or in special circumstances. There may be times when you will find yourself waiting long periods of time for your partner to return. Keep in mind that surveys can take two to three times as long during periods of heavy carcass processing and scale recovery. High flows also make surveys more time consuming. If, after taking these and any other relevant factors into account, you determine that your partner has been gone too long, it may be time to go looking for them. Before leaving the predetermined pick-up spot, leave a very visible note (use flagging or survey sheets). The note should state when you left and your exact search plan. Start your search by going in the exit route, and then downstream from the end to the start. The next step, if necessary, would be to contact your crew chief and the state police. Do not attempt this search by yourself if it is late in the day. If cell coverage allows, stay on site near the survey. Leave the site only if you have to do so to contact help. It is a good idea to keep a flashlight in the rig. Do not start surveys late in day that cannot be completed before dark.
• LANDOWNER DENIALS:
It may be possible to complete surveys with one or more denials. There may be past denials that the current description already takes into account. Surveys can be cut short at the start or end to avoid denied property. In some cases, small portions can be skipped. Creeks are often used as property boundaries. When landowners own only one side, the opposite bank can be walked to avoid the denied property. If you encounter denials while contacting landowners, do not automatically drop the survey. Unless a major landowner denies access, contact all landowners, and then check the feasibility of the survey. It will be necessary to use the tax maps to check exact property boundaries. Use caution and good judgment when conducting a survey with partial denials. Do not put yourself in a dangerous position. Consult with your crew chief prior to dropping a survey or deciding to do a survey with partial denials.
• CREEKS ARE UNSURVEYABLE:
Any creek with a visibility of 3 cannot be surveyed. Before making this determination, check several areas within the route. It is worthwhile to check several different spots - sometimes a creek may clear up a little way into the survey. If you cannot see more than a couple of inches into riffles or the tailouts of pools, you should not survey the creek.
There are a few guidelines that may help you during periods of high flows. Creeks have varying degrees of susceptibility to blowing out. If you know a big weather system is moving into the area, try to get the creeks that are more susceptible to blowing out done first. Once a storm has hit, focus on getting the smaller, less prone creeks done. Once the water level goes back down you can survey those creeks which you were not able to before. Planning and careful scheduling will help in keeping the surveys within the 10-day survey limit. It may be helpful to create a spreadsheet to help you plan. Consult regularly with your crew chief during periods of heavy rainfall when there are multiple creeks blown out. In general, when in doubt about the status of a creek go ahead and take the time to check it out.
57 Dealing with Special Circumstances (Continued)
• FISHING AND HUNTING REGULATIONS:
Two current copies of the ODFW fishing rules and regulations brochure can be found in the rig glovebox. Review the local regulations. Bear in mind that you are not an enforcement officer. If you encounter someone fishing illegally, use your best judgment on how to proceed. Often times it is just a matter of the fisherman not understanding or knowing the regulations. Suggesting a check of the regulations is often all it takes to get them to move on. Be careful about confrontations. If you do not feel comfortable approaching certain individuals, try to obtain relevant information such as a license plate number. Report illegal activity to the state police or your supervisor. Do not put yourself in a dangerous or an uncomfortable position.
• COHO SPAWNING IN SMALL TRIBUTARIES:
Random coho surveys should not be conducted beyond coho bearing tributaries with more than 100 linear meters of spawning habitat (from the mouth of the tributary running upstream). Those tributaries with less than 100 meters of habitat are known as Spur Tribs. Fish observed in Spur Tribs can be included in the counts for the parent stream. There are two variations on this scenario:
1) The description of a survey will include directions to walk up spur tributaries to the end of habitat (less than 100 meters). Any fish or redds found in spur tributaries will be included in the total count for the parent survey.
2) In some cases you may find coho spawning in tributaries within survey boundaries that are not mentioned in the survey description. In this case you should document that you saw fish spawning with the “Includes tributary to index” comment code, (01). Include the number of fish seen spawning in the tributary in your total count for the survey. Count only those fish and redds visible from the parent stream and do not venture up these streams as a spur. Consult with your crew chief on how to proceed in future surveys.
NOTE: If a tributary is found to have more than 100m of habitat, please notify your crew leader immediately.
Cell Phones
Some crews will be issued a cell phone. They are for work and emergency use only, not for routine personal calls, and should be taken with you in the vehicle every day. Check and respond to your messages daily. Be professional when answering the phone and when leaving your greeting.
Your crew chief or supervisor will help you set up your phone so that you can access your messages or leave a greeting.
58 PUBLIC RELATIONS AND SAFETY
When driving a state vehicle, accessing sites, or conducting surveys, you are personally representing ODFW to landowners, anglers, and the general public. In order to ensure continuing cooperation with our efforts, it is essential that we maintain a positive image and constructive relationships with members of the public.
If a landowner challenges your right to conduct surveys on their land, explain it was your understanding that permission was obtained, apologize for the misunderstanding, and request permission to continue the survey. Under no circumstances conduct a survey if the landowner denies you permission. If someone other than a landowner challenges your right to conduct a survey, tell him or her that you will seek confirmation of permission through the owner and your supervisor. Do not conduct a survey if you feel that it is unsafe to do so.
Always treat members of the public with respect. In recent years, ODFW has generally improved its public image, having demonstrated respect for landowners, a high level of scientific credibility, and budgetary responsibility. However, it is not uncommon to encounter a person who has complaints about ODFW or other fish and wildlife management issues. If you encounter an angry person and you feel unsafe, end the encounter. Otherwise, repeating or paraphrasing back what the person says will help you gain that person’s trust by letting them know that you hear and understand what they are saying. Find a point of agreement and end the conversation. Avoid prolonged discussions, you can always refer the individual to your supervisor if they want to follow up with more questions.
Be careful of other cars and trucks on the road, especially on logging roads. Generally, emergency vehicles, low boy trailers, log trucks, and pick-ups have the right-of-way in that order. Use your CB radio when you are on industrial forest roads! An example of how you might use your CB to warn unseen vehicles of your approach is “Milepost 17 up the Eighty-one Fifty-five Road”. You cannot count on other vehicles using their CBs.
Respect your physical and mental limits when conducting a survey. Don’t take unnecessary chances when walking across rapidly flowing streams, on slick rocks or bedrock, and on slick, unstable, or rotten logs. Stay aware of your surroundings at all times (that bear needs that salmon more than we need the data). Pay particular attention to fatigue or the potential for hypothermia, each will affect your judgment. You can probably make that jump across to the log 9 times out of 10, but it will be that one time you miss and slip that you’ll probably regret for the rest of the day if not the rest of the season.
Every workstation needs to have a surveyor check in system and search plan to locate missing surveyors.
We Would Rather Lose A Survey Than A Surveyor
AT ALL TIMES MAKE SAFETY YOUR TOP PRIORITY
59 STATE VEHICLES FOR OFFICIAL USE ONLY • Children and pets are not allowed in vehicles. • Smoking in vehicles is prohibited. • Operate vehicles in a safe manner at all times. • Always be courteous to other drivers (even knuckleheads and jerks). Fuel • Use State of Oregon Voyager credit card. • Make sure the vendor will take the card prior to purchase. • Vendor needs to record odometer reading for each fuel purchase. • Any purchases other than for fuel must be pre-approved prior to use of the credit card. Maintenance and Repairs • Have vehicle maintained (oil changes and fluids checked) on schedule (multiples of 5000 miles). The project can be fined if you exceed maintenance intervals. • Pre-authorize any service or repair by calling 1-800-378-0077 (0700-1800 M-F) • Voyager card may be accepted by some venders; ask first. • Keep vehicles clean! They also represent ODFW and must be presentable. At the end of the season, vehicles must be returned with the interior and exterior fully cleaned. The project will be charged if vehicles are returned dirty. ODFW MILEAGE REPORT (Vehicle Mileage Log) • Record each trip daily from the first of the month to the last day of the month. • At the end of each month turn in the white and yellow copy to your crew chief or send it to Lori Turner at the Corvallis Research Lab.
60 Personnel Policies and Procedures
Work Periods
Your work-week is defined by the Federal Fair Labor Standards Act. Accordingly, your normal workweek is 40 hours, beginning on Sunday and ending on Saturday. Your work schedule is irregular, meaning that the days you work during this period are not fixed. You will be compensated at time and one half for any hours worked in excess of 40 hours during each weekly work schedule, however overtime needs to be pre-approved by your project leader. Fill out a weekly Report of Operations Form to record your work hours and general work activities (see page 62).
Holidays and Leave
There are six paid holidays during the salmon spawning season: Veteran’s Day, Thanksgiving, Christmas, Governor’s add-on, New Year’s Day and Martin Luther King Day. In addition, ODFW employees earn eight hours of vacation and eight hours of sick leave per month, however vacation cannot be used until an employee has worked six months. Because of the short season, the unpredictable weather, and run timing conditions, extensive leave is not permitted. Employees will be paid unused vacation leave upon termination.
Benefits and Insurance
All employees appointed for 90 days or longer receive a monthly insurance contribution that can be applied to a “Cafeteria Style” benefits package. Benefit packets for enrollment are distributed in October or at the time of hiring. The choice of insurance coverage may result in additional cash back to the employee or additional out of pocket expenses. Work related injury or illness is covered through employer provided workers compensation insurance.
Accidents and Injuries
All employees are required to have an emergency medical notification form on file. Any on-the- job injuries must be reported to your supervisor within 24 hours. Your supervisor will help you complete an Accident and Incident Analysis form with 24 hours of being informed of the accident. If medical attention is required a SAIF Workers’ Compensation Claim Form 801 also needs to be completed and sent to SAIF within five days of the incident. If you are seen by a physician, you need to take a Physical Assessment Form to the physician’s office.
Crew chiefs have copies of the necessary documents and will help guide you through the process if you become injured. If you become injured and are unable to continue work in the field, we will attempt to find other types of work for you. Often this means Data Entry or other office assignment.
Vehicle accidents need to be reported to DAS as soon as possible. An accident form also needs to be filled out. Vehicle Accident Forms are located in the vehicle information packet assigned to each vehicle.
61 Personnel Policies and Procedures (continued)
Uniform Clothing
Employees are required to wear uniforms while working in the field. Uniforms may be worn only when on-duty. Newly hired seasonal employees shall be allowed a uniform allowance equal to the purchase of two uniform shirts with logo and one pair of pants. Seasonal employees working continuously for 10 months per fiscal year (June through July) will accrue an allowance of $25 per month of employment for use after an initial 6-month employment period. Returning seasonal employees shall receive credit for any unused allowance earned in the twelve months immediately preceding the rehire date. All purchases from this allowance must be pre-approved by the Project Leader. Uniform hats will be supplied to all employees and should be worn.
Purchasing
An itemized, dated and signed receipt is required for all purchases charged to the Agency. These receipts need to be sent to Karla Yeager, Purchasing Specialist at the Corvallis Research Lab, as soon as possible after purchase is made.
Pets and Volunteers
Pets are not allowed to accompany employees during fieldwork. Non-Department employees can accompany employees as volunteers for fieldwork. A completed and signed volunteer form needs to be on file prior to any work with volunteers.
Weapons
Possession or use of any weapon is strictly prohibited while on ODFW property (including vehicles) or while engaged in official agency business. This applies to both employees and volunteers.
Agency Policies Requiring Signatures
All employees are required to read and sign off on the following policies:
• Code of Conduct • Conflict of Interest/Ethics • Acceptable use of Electronic Equipment and Tools • Software Code of Ethics • Drug-Free Work Place
62 Report of Operations Form (example)
Complete daily to log activities and work hours
63 OREGON DEPARTMENT OF FISH AND WILDLIFE
REPORT OF OPERATIONS
Prepared by ______
Location ______
For the Week Ending ______
Date Activities
SUNDAY Month: Date:
MONDAY Month: Date:
TUESDAY Month: Date:
WEDNESDAY Month: Date:
THURSDAY Month: Date:
FRIDAY Month: Date:
SATURDAY Month Date:
TOTAL HOURS THIS WEEK: ______
64
Phone Listings
NAME TITLE NUMBER
Todd Alsbury North Willamette District Fisheries Biologist (503) 657-2000 ext 233 Danette Ehlers North Willamette Asst. Fish Biologist (503) 657-2000 ext.232
Rick Klumph North Coast District Manager (503) 842-2741 Keith Braun North Coast District Fish Biologist (503) 842-2741 Robert Bradley North Coast Asst. Fish Biologist (503) 338-0106
Bob Buckman Mid Coast District Fish Biologist (541) 867-4741 Derek Wilson Mid Coast Asst. Fish Biologist Newport (541) 867-4741 George Westfall Mid Coast Asst. Fish Biologist Mapleton (541) 902-1384
Jim Muck Umpqua District Fish Biologist (541) 440 3353 Sam Moyers Umpqua Asst. Fish Biologist (541) 440-3353
Mike Gray Coos-Coquille District Fish Biologist (541) 888-5515 Shannon Osbon Coos-Coquille Asst. Fish Biologist (541) 888-5515
Todd Confer South Coast District Biologist (541) 247 7605 Steve Mazur South Coast Assistant Fish Biologist (541) 247 7605 Dan VanDyke Upper Rogue District Biologist (541) 826-8774 Dave Haight Upper Rogue Asst. Central Point (541) 826-8774
Kelly Moore NW Region Research Program Manager (541) 757-4263 ext 226 Mark Lewis OASIS Inventory Acting Project Leader (541) 757-4263 ext 241 Gary Susac OASIS Inventory Asst. Project Leader (541) 757-4263 ext 248 Briana Sounhein OASIS Inventory Asst. Project Leader (541) 757-4263 ext 227 Erik Suring OASIS Lower Columbia Asst. Project Leader (541) 757-4263 ext 264 LaNoah Babcock OASIS Data Administration (541) 757-4263 ext 269
Brian Riggers Chinook Studies Project Biologist (541) 757-4263 ext 265 Lisa Borgerson Scale Reading Project Leader (541) 757-4263 ext 232
Dave Stewart Crew Chief for North Coast and Tillamook (541) 760-7513 Pat Burns Crew Chief for Umpqua, Coos-Coquille, South (541) 760-7768 Eric Brown Acting Crew Chief for Lower Columbia (541) 757-4263
65 66 North Coast 4th Field HUC's
!! ! ! !! ! ! ! ! ! ! ! ! ! ! NEHALEM ! ! ! ! ! ! !! NECANICUM ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! !! ! ! !! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! !! ! ! ! ! ! ! ! ! ! ! ! ! !! ! ! ! ! ! WILSON-TRASK-NESTUCCA ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! !! !! ! ! Mid Coast 4th Field HUC's !! ! ! ! ! ! ! ! !
SILETZ-YAQUINA
! ! ! ! ! !! ! ! ! ! ! ! ! !! ! ! ! !! ! ! !
!! ! ALSEA ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! !!! ! ! ! ! ! ! ! ! ! ! ! ! ! ! SIUSLAW ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! SILTCOOS ! ! ! ! ! ! ! ! ! ! ! ! ! ! !! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! !! Mid-South Coast 4th Field HUC's ! ! ! ! ! ! ! ! ! ! ! SILTCOOS ! ! ! ! ! ! ! ! ! ! ! ! !! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! !! UMPQUA ! ! ! ! !! ! COOS ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! !! ! ! ! ! ! !! ! ! ! ! !! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! !! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! !! ! ! ! ! ! ! ! COQUILLE ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! !! ! !! ! ! ! ! ! SIXES ! ! ! ! ! ! ! ! ! ! ! ! Umpqua 4th Field HUC's
! ! ALSEA ! ! ! ! ! ! ! !! ! ! ! !! ! ! ! ! ! ! ! ! !! ! ! ! ! ! ! ! !!! ! ! ! ! ! ! ! !!! ! ! SIUSLAW !! ! ! ! ! ! ! ! ! ! ! ! ! ! SILTCOOS ! ! ! ! !! ! ! ! ! ! ! ! ! ! !! ! !!! ! ! ! ! ! ! ! ! ! ! ! ! !! ! ! ! ! ! ! ! ! !!! !! ! ! ! ! ! !!! UMPQUA ! ! ! ! ! COOS ! !!! ! ! ! ! ! ! ! ! !! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! !! ! ! ! ! ! ! ! ! ! ! ! ! ! !! ! ! !! !! ! ! !! ! ! ! ! ! ! !! ! ! !!!!! ! ! ! ! ! ! ! ! NORTH UMPQUA ! ! ! !! ! ! ! ! ! ! ! ! ! ! ! !! !! ! COQUILLE ! ! !! ! !! ! ! ! ! ! ! !! ! ! ! ! ! ! ! ! SOUTH UMPQUA ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! !!! ! ! ! !
UPPER ROGUE LOWER ROGUE
MIDDLE ROGUE
ILLINOIS CHETCO APPLEGATE South Coast 4th Field HUC's
SILTCOOS! !!! !! ! ! ! !!! !!!! ! ! ! !! ! ! !! !!! ! ! ! ! ! ! ! !! ! !!! ! ! ! !!! !! ! !! ! ! ! !! UMPQUA ! !! ! ! COOS! !!!! !! ! ! ! ! ! ! !! ! !! !! ! ! !! ! ! !!! ! !! !! !! ! ! ! ! ! ! ! ! !! ! ! !! !! ! ! ! ! !!! !!! !! !!!!!! !!! ! ! ! ! ! ! NORTH UMPQUA ! !! ! ! ! ! !! ! ! ! ! ! ! ! !! ! ! ! !! ! !!!COQUILLE!! ! ! ! !! !! ! ! !! ! !!! ! ! ! ! ! ! !! !! ! ! ! ! ! !! SOUTH UMPQUA ! ! ! ! ! ! ! ! ! ! ! ! SIXES ! ! ! ! ! ! ! ! ! ! ! ! !! ! ! ! ! ! !
! LOWER ROGUE UPPER ROGUE !! ! ! ! MIDDLE ROGUE ILLINOIS CHETCO APPLEGATE North Coast 2005-2006 Spawning Surveys Basin Subbasin Reach ID Seg. Survey Name Type Species Status Year(s) Surv. Miles Necanicum River Mainstem 26196.00 1 Little Muddy Cr Random Coho New 05 0.50 Necanicum River Mainstem 26204.00 2 Circle Creek Random Coho Repeat 98,99,00,01,02,03,04,05 1.14 Necanicum River Mainstem 26204.00 2 Circle Creek Random Steelhead 03,04,05,06 1.14 Necanicum River Mainstem 26205.00 2.1 Necanicum Chum - Lower Supplemental Chum 00,01,02,03,04,05 1.10 Necanicum River Mainstem 26205.30 1 Diehl Cr Random Coho Repeat 94,99,02,05 0.72 Necanicum River Mainstem 26205.30 1 Diehl Cr Random Steelhead 03,06 0.72 Necanicum River Mainstem 26211.00 1.1 Necanicum - upper Supplemental Chum 00,01,02,03,04,05 2.00 Necanicum River Mainstem 26228.00 2 Necanicum R, N Fk Random Coho Repeat 93,98,99,00,01,02,03,04, 1.20 Necanicum River Mainstem 26228.70 1 Necanicum R, N Fk Random Coho Repeat 91,97,99,02,05 0.98 Necanicum River Mainstem 26231.00 1 Necanicum R Random Coho New 05 0.60 Necanicum River Mainstem 26231.00 1 Necanicum R Random Steelhead 06 0.60 Necanicum River Mainstem 26239.00 1 Joe Cr Random Coho Repeat 96,98,99,01,02,03,04,05 1.11 Necanicum River Mainstem 26243.00 2 Upper NecanicumR (Standard) Standard Coho Annual 1.50 Necanicum River Mainstem 26244.00 1 Grindy Cr Random Coho New 05 0.60 Necanicum River Mainstem 26244.00 1 Grindy Cr Random Steelhead 06 0.60 Necanicum River South Fork 26220.00 1 Necanicum R, S Fk (Mouth To Random Coho Repeat 99,00,02,05 0.56 Brandis Cr) Necanicum River Neawanna Cr 26192.70 2 Thompson Cr Random Coho New 05 0.40 Necanicum River Neawanna Cr 26192.70 2 Thompson Cr Random Steelhead 06 0.40 Necanicum River Neawanna Cr 26193.40 2 Neawanna Cr Random Coho Repeat 98,05 1.24 Necanicum River Neawanna Cr 26193.40 2 Neawanna Cr Random Steelhead 06 1.24 Ecola Creek North Fork 26183.00 2 Ecola Cr, N Fk Random Coho Repeat 93,05 1.31 Ecola Creek West Fork 26182.00 2 W Fk Ecola (Elk) Creek Standard Coho Annual 0.50 Nehalem River Mainstem 25833.50 1 Neahkahnie Cr Random Coho New 05 0.90 Nehalem River Mainstem 25835.00 1 Bobs Creek Supplemental Chum 94,95,96,97,98,99,00,01, 0.70 Nehalem River Mainstem 25887.20 2 Daniels Cr Random Coho Repeat 99,02,05 0.49 Nehalem River Mainstem 25888.00 1 East Foley Creek Supplemental Chum 94,95,96,97,98,99,00,01, 1.00 Nehalem River Mainstem 25889.00 1 Foley Cr Random Coho Repeat 98,99,00,01,02,03,04,05 1.24 Nehalem River Mainstem 25889.00 1 Foley Cr Random Steelhead 03,06 1.24 Nehalem River Mainstem 25893.00 1 Foley Cr Random Coho Repeat 92,05 1.10 Nehalem River Mainstem 25893.00 1 Foley Cr Random Steelhead 06 1.10 Nehalem River Mainstem 25907.00 1 Cook Creek Standard Fall Chinook Annual 1.00 Nehalem River Mainstem 25907.00 1 Cook Creek Random Coho Repeat 97,04,05 1.00 Nehalem River Mainstem 25907.00 1 Cook Creek Random Steelhead 05,06 1.00 Nehalem River Mainstem 25911.00 1 Cook Creek Random Coho Repeat 05 0.86 Nehalem River Mainstem 25919.00 2 Fall Cr Random Coho New 05 0.90 North Coast 2005-2006 Spawning Surveys Basin Subbasin Reach ID Seg. Survey Name Type Species Status Year(s) Surv. Miles Nehalem River Mainstem 25921.00 2 Helloff Cr Random Coho New 05 0.80 Nehalem River Mainstem 25921.00 2 Helloff Cr Random Steelhead 06 0.80 Nehalem River Mainstem 25958.00 2 Cronin Cr, N Fk Random Coho Repeat 99,00,02,03,05 0.53 Nehalem River Mainstem 25959.00 1 Cronin Creek Standard Fall Chinook Annual 1.00 Nehalem River Mainstem 25967.00 2.1 Humbug Creek Standard Fall Chinook Annual 1.00 Nehalem River Mainstem 25980.00 1 East Humbug Creek Standard Fall Chinook Annual 1.18 Nehalem River Mainstem 25980.00 2 E Humbug Cr Random Coho Repeat 02,03,05 1.35 Nehalem River Mainstem 25980.00 2 E Humbug Cr Random Steelhead 06 1.35 Nehalem River Mainstem 25982.70 2 Beaver Cr Random Coho New 05 0.70 Nehalem River Mainstem 25985.00 1 W Humbug Cr Random Coho Repeat 90,91,98,99,00,01,02,03, 1.00 Nehalem River Mainstem 25995.00 5 Cow Cr Random Coho New 05 0.30 Nehalem River Mainstem 25999.00 2 Moores Cr Random Coho Repeat 97,05 0.97 Nehalem River Mainstem 25999.00 2 Moores Cr Random Steelhead 06 0.97 Nehalem River Mainstem 26003.00 1 Buster Cr Random Coho Repeat 97,05 1.10 Nehalem River Mainstem 26003.00 1 Buster Cr Random Steelhead 06 1.10 Nehalem River Mainstem 26013.00 1 Walker Cr Random Coho New 05 1.20 Nehalem River Mainstem 26016.00 3 Beneke Cr Random Coho New 05 1.60 Nehalem River Mainstem 26016.00 3 Beneke Cr Random Steelhead 06 1.60 Nehalem River Mainstem 26024.00 3 Hamilton Cr. Random Coho Repeat 91,97,05 1.00 Nehalem River Mainstem 26024.00 3 Hamilton Cr. Random Steelhead 06 1.00 Nehalem River Mainstem 26033.30 1 Cow Cr Random Coho Repeat 99,02,05 0.95 Nehalem River Mainstem 26033.30 2 Cow Cr Random Coho Repeat 92,94,97,03,05 1.20 Nehalem River Mainstem 26033.50 3 Northrup Cr Random Coho Repeat 94,00,05 1.04 Nehalem River Mainstem 26043.00 2 Deep Cr Random Coho Repeat 98,99,01,02,04,05 0.85 Nehalem River Mainstem 26050.00 1 Fishhawk Cr, North Fork Random Coho Repeat 05 0.58 Nehalem River Mainstem 26050.00 1 Fishhawk Cr, North Fork Random Steelhead 06 0.58 Nehalem River Mainstem 26051.00 1 Fishhawk Cr Random Coho Repeat 93,94,05 0.76 Nehalem River Mainstem 26051.00 1 Fishhawk Cr Random Steelhead 06 0.76 Nehalem River Mainstem 26057.00 1 Ford Cr (Lindgren Cr) Random Coho Repeat 95,99,00,02,03,05 0.95 Nehalem River Mainstem 26057.00 1 Ford Cr (Lindgren Cr) Random Steelhead 03,06 0.95 Nehalem River Mainstem 26057.00 4 Ford Cr Random Coho New 05 1.30 Nehalem River Mainstem 26057.00 4 Ford Cr Random Steelhead 06 1.30 Nehalem River Mainstem 26057.00 5 Ford Cr Random Coho Repeat 00,05 0.62 Nehalem River Mainstem 26061.00 3 Lundgren Cr Random Coho Repeat 97,98,99,00,01,02,03,04, 1.38 Nehalem River Mainstem 26075.00 1 Oak Ranch Cr Random Coho Repeat 96,99,05 1.01 Nehalem River Mainstem 26077.00 2 Oak Ranch Cr Random Coho Repeat 99,00,05 1.32 North Coast 2005-2006 Spawning Surveys Basin Subbasin Reach ID Seg. Survey Name Type Species Status Year(s) Surv. Miles Nehalem River Mainstem 26077.00 3 Oak Ranch Cr Random Coho Repeat 99,02,05 0.96 Nehalem River Mainstem 26077.00 4 Oak Ranch Cr Random Coho New 05 1.10 Nehalem River Mainstem 26077.00 4 Oak Ranch Cr Random Steelhead 06 1.10 Nehalem River Mainstem 26081.00 2 Crooked Cr Random Coho Repeat 90,91,95,96,98,99,00,01, 1.20 Nehalem River Mainstem 26081.00 2 Crooked Cr Random Steelhead 03,06 1.20 Nehalem River Mainstem 26092.00 1 Jim George Cr Random Coho Repeat 97,03,05 1.46 Nehalem River Mainstem 26092.00 3 Jim George Cr Random Coho Repeat 01,05 0.54 Nehalem River Mainstem 26092.00 3 Jim George Cr Random Steelhead 06 0.54 Nehalem River Mainstem 26093.30 1 E Fk Neh., Unnamed Trib A Random Coho Repeat 98,99,00,01,02,03,04,05 1.03 Nehalem River Mainstem 26093.30 1 E Fk Neh., Unnamed Trib A Random Steelhead 03,04,05,06 1.03 Nehalem River Mainstem 26123.00 1 Pebble Cr Random Coho New 05 0.90 Nehalem River Mainstem 26123.00 2 Pebble Cr Random Coho Repeat 99,02,05 1.01 Nehalem River Mainstem 26123.00 2 Pebble Cr Random Steelhead 03,06 1.01 Nehalem River Mainstem 26124.70 1 Coal Cr Random Coho Pending 05 Nehalem River Mainstem 26125.00 2 Pebble Cr Random Coho Repeat 98,99,00,01,02,03,05 0.28 Nehalem River Mainstem 26125.00 2 Pebble Cr Random Steelhead 03,04,06 0.28 Nehalem River Mainstem 26137.00 1 Clear Cr Random Coho Repeat 00,03,05 1.09 Nehalem River Mainstem 26139.00 1 Robinson Cr Random Coho Repeat 99,05 1.03 Nehalem River Mainstem 26139.00 1 Robinson Cr Random Steelhead 06 1.03 Nehalem River Mainstem 26142.00 2 Wolf Cr, N Fk Random Coho New 05 0.70 Nehalem River Mainstem 26146.00 2 Lousignont Creek, North Fork Random Coho Repeat 03,05 1.20 Nehalem River Mainstem 26146.00 2 Lousignont Creek, North Fork Random Steelhead 04,06 1.20 Nehalem River Mainstem 26147.30 1 Carlson Creek Random Coho Repeat 04,05 1.60 Nehalem River North Fork 25840.00 2 Coal Creek (Chum) Supplemental Chum 94,95,96,97,98,99,00,01, 1.20 Nehalem River North Fork 25864.00 1 Soapstone Cr Standard Fall Chinook Annual 0.69 Nehalem River North Fork 25868.00 1 Soapstone Creek Random Coho Repeat 05 1.40 Nehalem River North Fork 25869.00 1 Soapstone Cr, Trib A Random Coho Repeat 98,99,00,01,02,03,04,05 0.80 Nehalem River North Fork 25869.00 1 Soapstone Cr, Trib A Random Steelhead 03,04,05,06 0.80 Nehalem River North Fork 25879.00 1 Nehalem R, N Fk Random Coho Repeat 96,98,99,00,01,02,03,04, 1.25 Nehalem River North Fork 25879.00 1 Nehalem R, N Fk Random Steelhead 03,04,05,06 1.25 Nehalem River North Fork 25879.40 1 Nehalem R, N Fk (Trib R To Random Coho Repeat 05 0.95 Trib T) Nehalem River North Fork 25879.40 1 Nehalem R, N Fk (Trib R To Random Steelhead 06 0.95 Trib T) Nehalem River North Fork 25880.00 5 Little N. Fk Nehalem (Log Br. Random Coho Repeat 05 1.19 To Fork) Nehalem River North Fork 25881.00 4 Nehalem R, N Fk Random Coho New 05 0.70 North Coast 2005-2006 Spawning Surveys Basin Subbasin Reach ID Seg. Survey Name Type Species Status Year(s) Surv. Miles Nehalem River Salmonberry River 25931.00 2 Salmonberry River Standard Fall Chinook Annual 0.50 Nehalem River Rock Creek 26100.00 1 Maynard Cr Random Coho Repeat 98,99,00,01,02,03,04,05 1.14 Nehalem River Rock Creek 26100.00 1 Maynard Cr Random Steelhead 03,04,05,06 1.14 Nehalem River Rock Creek 26107.00 3 Rock Cr Random Coho Repeat 92,99,00,02,05 0.98 Nehalem River Rock Creek 26110.00 2 Weed Cr Random Coho Repeat 93,97,99,01,05 1.60 Nehalem River Rock Creek 26110.00 2 Weed Cr Random Steelhead 06 1.60 Nehalem River Rock Creek 26111.90 1 Rock Cr Random Coho Repeat 97,99,02,05 1.08 Nehalem River Rock Creek 26115.00 1 Rock Cr, S Fk Random Coho Repeat 03,05 1.46 Nehalem River Rock Creek 26117.00 2 Rock Cr, S.Fk. Random Coho Repeat 98,99,00,01,02,03,04,05 1.24 Nehalem River Rock Creek 26117.50 1 Rock Cr Random Coho Repeat 95,05 0.57 Nehalem River Rock Creek 26117.50 1 Rock Cr Random Steelhead 06 0.57 Tillamook 2005-2006 Spawning Surveys Basin Subbasin Reach ID Seg. Survey Name Type Species Status Year(s) Surv. Miles Miami River Mainstem 25787.00 1 Moss Creek Standard Chum Annual 0.50 Miami River Mainstem 25790.00 1 Miami River Standard Chum Annual 0.46 Miami River Mainstem 25795.00 1 Stuart Cr Random Coho Repeat 98,99,00,01,02,03,04,05 1.24 Miami River Mainstem 25797.00 1 Prouty Cr Standard Chum Annual 0.40 Miami River Mainstem 25800.00 1 Miami R Random Coho Repeat 96,98,99,05 1.44 Miami River Mainstem 25800.00 1 Miami R Random Steelhead 06 1.44 Kilchis River Mainstem 25719.00 1 Coal Creek Supplemental Chum 95,96,97,98,99,00,01,02, 0.50 Kilchis River Mainstem 25719.00 2 Coal Creek Standard Chum Annual 0.50 Kilchis River Mainstem 25719.00 3 Coal Cr Random Coho Repeat 98,99,00,01,02,03,04,05 0.71 Kilchis River Mainstem 25722.00 2 Kilchis River Standard Chum Annual 1.00 Kilchis River Mainstem 25729.00 1 Clear Creek Standard Fall Chinook Annual 0.60 Kilchis River Mainstem 25729.00 1 Clear Creek Standard Chum Annual 0.60 Kilchis River Mainstem 25763.00 2 Kilchis R, N Fk Random Coho Repeat 96,00,01,02,03,04,05 0.99 Kilchis River Mainstem 25763.00 2 Kilchis R, N Fk Random Steelhead 03,06 0.99 Kilchis River Little South Fork 25733.00 1 Little South Fork Standard Fall Chinook Annual 1.00 Kilchis River Little South Fork 25740.00 1 Sam Downs Creek Standard Coho Annual 1.00 Wilson River Mainstem 25671.00 1 Muesial Cr Random Coho New 05 0.10 Wilson River Mainstem 25675.00 1 Jordan Cr Random Coho Repeat 96,05 0.98 Wilson River Mainstem 25675.50 4 Jordan Cr Random Coho Repeat 97,98,99,00,01,02,03,04, 0.91 Wilson River Mainstem 25679.00 1 Cedar Cr Standard Fall Chinook Annual 2.80 Wilson River Mainstem 25679.00 1 Cedar Cr Standard Coho Annual 2.80 Wilson River Mainstem 25679.00 1 Cedar Cr Random Coho Repeat 94,95,96,99,01,02,05 2.80 Wilson River Mainstem 25695.00 1 Ben Smith Cr Random Coho Repeat 96,98,99,00,01,02,03,04, 0.42 Wilson River Mainstem 25695.00 1 Ben Smith Cr Random Steelhead 03,04,05,06 0.42 Wilson River Mainstem 25695.90 1 Ben Smith Cr Random Coho Repeat 99,02,05 0.59 Wilson River Mainstem 25703.00 1 Elk Cr Random Coho Repeat 91,92,94,96,02,05 1.00 Wilson River Little North Fork 25641.00 1 L N Fk Wilson R Standard Fall Chinook Annual 0.50 Wilson River Little North Fork 25641.00 1 L N Fk Wilson R Standard Chum Annual 0.50 Wilson River North Fork 25687.50 1 Wilson R, N Fk, Trib A Random Coho Repeat 99,02,05 0.78 Wilson River North Fork 25688.70 1 Wilson R, Wf Of Nf Random Coho Repeat 92,03,05 1.35 Wilson River North Fork 25689.00 2 Wilson R, N Fk Random Coho Repeat 96,97,99,02,05 1.34 Wilson River North Fork 25689.00 2 Wilson R, N Fk Random Steelhead 03,06 1.34 Wilson River South Fork 25705.00 2 Wilson River, S Fk Random Coho Repeat 97,05 0.51 Wilson River Devil's Lake Fork 25714.00 1 Wilson R, Devil'S Lake Fk Random Coho Repeat 96,05 1.20 Wilson River Devil's Lake Fork 25716.00 2 Wilson R, Devils Lake Fork Random Coho Repeat 95,98,05 0.97 Wilson River Devil's Lake Fork 25716.00 2 Wilson R, Devils Lake Fork Random Steelhead 06 0.97 Tillamook 2005-2006 Spawning Surveys Basin Subbasin Reach ID Seg. Survey Name Type Species Status Year(s) Surv. Miles Trask River Mainstem 25585.00 2 Mill Cr Random Coho Repeat 96,97,99,00,02,03,05 0.74 Trask River Mainstem 25603.00 1 Rawe Cr Random Coho Repeat 99,02,05 0.94 Trask River North Fork 25619.00 2 Hembre Cr (Clear Cr, #1) Random Coho Repeat 97,05 0.94 Trask River North Fork 25623.00 1 Clear Cr #2 Random Coho Repeat 94,99,02,05 1.10 Trask River North Fork 25623.00 1 Clear Cr #2 Random Steelhead 03,06 1.10 Trask River South Fork 25608.30 1 Boundry Cr Random Coho Repeat 98,99,00,01,02,03,04,05 0.64 Trask River South Fork 25608.30 1 Boundry Cr Random Steelhead 03,04,05,06 0.64 Trask River South Fork 25608.60 2 Trask R, S Fk, E Fk Random Coho New 05 0.70 Trask River South Fork 25608.60 2 Trask R, S Fk, E Fk Random Steelhead 06 0.70 Trask River South Fork 25612.00 4 Edwards Cr Random Coho New 05 0.70 Trask River South Fork 25612.00 4 Edwards Cr Random Steelhead 06 0.70 Tillamook River Mainstem 25559.00 3 Bewley Cr Random Coho Repeat 90,95,96,97,99,02,05 0.97 Tillamook River Mainstem 25559.00 3 Bewley Cr Random Steelhead 03,06 0.97 Tillamook River Mainstem 25560.00 1 Tillamook R Random Coho Repeat 95,99,02,05 0.85 Tillamook River Mainstem 25564.00 1 Tillamook River Standard Fall Chinook Annual 1.80 Tillamook River Mainstem 25565.00 2 Simmons Cr Standard Fall Chinook Annual 0.60 Tillamook River Mainstem 25565.00 2 Simmons Cr Standard Coho Annual 0.60 Tillamook River Mainstem 25565.00 3 Simmons Cr Random Coho Repeat 96,97,99,00,02,05 1.49 Tillamook River Mainstem 25565.00 3 Simmons Cr Random Steelhead 03,06 1.49 Tillamook River Mainstem 25571.00 1 Mills Cr Random Coho Repeat 93,05 0.52 Tillamook River Mainstem 25571.00 1 Mills Cr Random Steelhead 06 0.52 Netarts Bay Mainstem 25543.00 1 Whiskey Creek Supplemental Chum 94,95,96,97,98,99,00,01, 0.50 Nestucca River Mainstem And Bay 25407.00 2 Clear Cr, Queens Cr To Standard Fall Chinook Annual 0.80 Headwaters Nestucca River Mainstem And Bay 25407.00 2 Clear Cr, Queens Cr To Standard Coho Annual 0.80 Headwaters Nestucca River Mainstem And Bay 25407.00 2 Clear Cr, Queens Cr To Standard Chum Annual 0.80 Headwaters Nestucca River Mainstem And Bay 25409.00 1 Sanders Cr (Smith Cr) Random Coho Repeat 99,05 0.74 Nestucca River Mainstem And Bay 25409.00 1 Sanders Cr (Smith Cr) Random Steelhead 06 0.74 Nestucca River Mainstem And Bay 25435.00 1 Farmer Cr, Mouth To Trib A Random Coho Repeat 92,97,05 0.95 Nestucca River Mainstem And Bay 25435.00 1 Farmer Cr, Mouth To Trib A Random Steelhead 06 0.95 Nestucca River Mainstem And Bay 25456.00 1 Foland Cr, W Fk Random Coho Repeat 97,98,05 1.02 Nestucca River Mainstem And Bay 25456.00 1 Foland Cr, W Fk Random Steelhead 06 1.02 Nestucca River Mainstem And Bay 25459.00 1 Wolfe Cr, Mouth To Swab Cr Random Coho Repeat 92,99,02,05 0.69 Nestucca River Mainstem And Bay 25459.00 1 Wolfe Cr, Mouth To Swab Cr Random Steelhead 03,06 0.69 Nestucca River Mainstem And Bay 25469.00 1 Bays Cr Supplemental Fall Chinook Annual 0.72 Tillamook 2005-2006 Spawning Surveys Basin Subbasin Reach ID Seg. Survey Name Type Species Status Year(s) Surv. Miles Nestucca River Mainstem And Bay 25474.00 1 East Cr Random Coho New 05 1.00 Nestucca River Mainstem And Bay 25474.00 1 East Cr Random Steelhead 06 1.00 Nestucca River Mainstem And Bay 25481.00 1 Powder Cr, Mouth To Left Random Coho Repeat 91,94,95,98,99,00,01,02, 1.10 Branch Nestucca River Mainstem And Bay 25482.50 1 Powder Cr, Left Branch To Dahl Random Coho Repeat 98,99,00,01,02,03,04,05 0.92 Fork Nestucca River Mainstem And Bay 25482.50 1 Powder Cr, Left Branch To Dahl Random Steelhead 01,02,03,04,05,06 0.92 Fork Nestucca River Mainstem And Bay 25485.00 1 Niagara Cr, Mouth To Beulah Cr Standard Fall Chinook Annual 0.40 Nestucca River Mainstem And Bay 25486.00 2 Beulah Cr Random Coho Repeat 96,97,00,05 1.18 Nestucca River Mainstem And Bay 25486.00 2 Beulah Cr Random Steelhead 01,06 1.18 Nestucca River Mainstem And Bay 25503.00 1 Bear Cr Random Coho Repeat 98,99,00,01,02,03,04,05 1.42 Nestucca River Mainstem And Bay 25503.00 1 Bear Cr Random Steelhead 01,02,03,04,05,06 1.42 Nestucca River Three Rivers 25419.00 1 Pollard Cr Random Coho Repeat 97,99,05 1.02 Nestucca River Three Rivers 25419.00 1 Pollard Cr Random Steelhead 06 1.02 Nestucca River Three Rivers 25424.00 2 Buck Cr Random Coho Repeat 97,99,02,05 0.48 Nestucca River Three Rivers 25424.00 2 Buck Cr Random Steelhead 03,06 0.48 Nestucca River Three Rivers 25426.00 1 Three Rivers, Alder Cr To Crazy Random Coho Repeat 97,98,99,00,01,02,03,04, 1.34 Cr Nestucca River Three Rivers 25426.00 1 Three Rivers, Alder Cr To Crazy Random Steelhead 01,02,03,04,05,06 1.34 Cr Nestucca River Beaver Creek 25451.00 2 E. Beaver Cr, Wildcat Cr To Random Coho Repeat 94,98,99,01,04,05 1.06 Headwaters Nestucca River Beaver Creek 25451.00 2 E. Beaver Cr, Wildcat Cr To Random Steelhead 02,05,06 1.06 Headwaters Nestucca River Beaver Creek 25451.00 6 E. Beaver Cr, Wildcat Cr To Random Coho Repeat 98,00,01,02,03,04,05 0.81 Headwaters Nestucca River Beaver Creek 25451.00 6 E. Beaver Cr, Wildcat Cr To Random Steelhead 01,02,03,04,05,06 0.81 Headwaters Nestucca River Beaver Creek 25451.00 8 E Beaver Cr Random Coho Repeat 05 0.80 Nestucca River Beaver Creek 25451.00 8 E Beaver Cr Random Steelhead 06 0.80 Nestucca River Little Nestucca 25358.00 1 Kellow Cr Random Coho New 05 0.40 Nestucca River Little Nestucca 25358.00 1 Kellow Cr Random Steelhead 06 0.40 Nestucca River Little Nestucca 25377.00 1 Little Nestucca R, Cedar Cr To Random Coho Repeat 98,99,00,01,02,03,04,05 0.76 Louie Cr Nestucca River Little Nestucca 25377.00 1 Little Nestucca R, Cedar Cr To Random Steelhead 01,02,03,04,05,06 0.76 Louie Cr Nestucca River Little Nestucca 25378.00 1 Louie Cr Random Coho New 05 0.60 Nestucca River Little Nestucca 25378.00 1 Louie Cr Random Steelhead 06 0.60 Tillamook 2005-2006 Spawning Surveys Basin Subbasin Reach ID Seg. Survey Name Type Species Status Year(s) Surv. Miles Tillamook Bay Mainstem And Bay 25774.00 1 Patterson Cr Random Coho Repeat 92,05 0.60 Tillamook Bay Mainstem And Bay 25774.00 1 Patterson Cr Random Steelhead 06 0.60 Neskowin Creek Mainstem 25331.00 3 Butte Cr Random Coho Pending 05 Neskowin Creek Mainstem 25331.00 3 Butte Cr Random Steelhead 06 Neskowin Creek Mainstem 25341.00 1 Lewis Cr Random Coho New 05 1.10 Neskowin Creek Mainstem 25341.00 1 Lewis Cr Random Steelhead 06 1.10 Neskowin Creek Mainstem 25343.70 1 Sloan Cr Random Coho Repeat 97,98,99,00,01,02,03,04, 0.25 Neskowin Creek Mainstem 25343.70 1 Sloan Cr Random Steelhead 03,04,05,06 0.25 Lincoln 2005-2006 Spawning Surveys Basin Subbasin Reach ID Seg. Survey Name Type Species Status Year(s) Surv. Miles Salmon River Mainstem And Bay 25266.70 1 Crowley Cr Random Coho Repeat 99,02,05 0.54 Salmon River Mainstem And Bay 25272.00 1 Salmon Creek #2 Random Coho Repeat 97,00,03,05 0.57 Salmon River Mainstem And Bay 25288.00 1 Willis Cr Random Coho Repeat 90,05 0.34 Salmon River Mainstem And Bay 25292.00 1 Panther Cr Random Coho Repeat 92,94,98,99,00,01,02,03, 1.02 Salmon River Mainstem And Bay 25296.00 1 Bear Creek (Lower) Supplemental Fall Chinook 94,95,96,97,98,99,00,01, 2.00 Salmon River Mainstem And Bay 25296.00 2 Bear Cr (Middle) Supplemental Fall Chinook 94,95,96,97,98,99,00,01, 1.40 Salmon River Mainstem And Bay 25296.00 2 Bear Cr (Middle) Random Coho Repeat 92,93,96,98,04,05 1.40 Salmon River Mainstem And Bay 25296.00 2 Bear Cr (Middle) Random Steelhead 06 1.40 Salmon River Mainstem And Bay 25300.00 1 Slick Rock Cr Random Coho Repeat 92,98,99,00,01,02,03,04, 1.00 Salmon River Mainstem And Bay 25313.00 1 Prairie Cr Random Coho New 05 0.90 Salmon River Mainstem And Bay 25313.00 1 Prairie Cr Random Steelhead 06 0.90 Devil's Lake Mainstem 25263.00 3 Rock Creek Supplemental Coho 94,95,96,97,98,99,00,01, 1.00 Devil's Lake Mainstem 25263.00 4 (Upper) Rock Cr Supplemental Coho 94,95,96,97,98,99,00,01, 1.00 Siletz River Mainstem 25091.00 1 Stemple Cr Random Coho Repeat 93,96,02,05 0.90 Siletz River Mainstem 25091.00 1 Stemple Cr Random Steelhead 06 0.90 Siletz River Mainstem 25101.00 2 Jaybird Cr Random Coho Repeat 93,96,05 1.30 Siletz River Mainstem 25101.00 2 Jaybird Cr Random Steelhead 06 1.30 Siletz River Mainstem 25102.50 1 Cedar Cr Standard Fall Chinook Annual 1.60 Siletz River Mainstem 25105.00 1 Euchre Cr, Mouth To Savage Cr Standard Fall Chinook Annual 1.00 Siletz River Mainstem 25131.70 2 Sam Cr Random Coho Repeat 90,94,98,99,00,01,02,03, 0.52 Siletz River Mainstem 25149.00 1 Mill Creek, Siletz (Cerine To Supplemental Coho 99,00,01,02,03,04,05 1.51 Gunn) Siletz River Mainstem 25149.30 1 Gunn Creek Supplemental Coho 00,01,02,03,04,05 0.85 Siletz River Mainstem 25149.70 1 Mill Cr (Gunn To Forks) Supplemental Coho 99,00,01,02,03,04,05 0.87 Siletz River Mainstem 25150.00 1 Mill Cr, S Fk Supplemental Coho 99,00,01,02,03,04,05 0.77 Siletz River Mainstem 25150.00 2 Mill Cr, S Fk Supplemental Coho 00,01,02,03,04,05 1.02 Siletz River Mainstem 25150.00 2 Mill Cr, S Fk Random Coho Repeat 96,98,01,04,05 1.02 Siletz River Mainstem 25150.00 2 Mill Cr, S Fk Random Steelhead 06 1.02 Siletz River Mainstem 25151.00 1 Mill Cr, N Fk Random Coho Repeat 98,99,00,01,02,03,04,05 1.38 Siletz River Mainstem 25151.00 1 Mill Cr, N Fk Random Steelhead 03,06 1.38 Siletz River Mainstem 25159.00 1 Buck Cr. Random Coho Repeat 98,99,00,01,02,03,04,05 0.49 Siletz River Mainstem 25159.00 1 Buck Cr. Random Steelhead 03,04,05,06 0.49 Siletz River Mainstem 25159.00 1 Buck Cr. Random Fall Chinook 05 0.49 Siletz River Mainstem 25160.00 1 Buck Cr, E Fk Random Coho Repeat 95,05 0.77 Siletz River Mainstem 25165.00 1 Sunshine Cr Standard Fall Chinook Annual 1.20 Siletz River Mainstem 25168.00 1 Fourth Of July Cr Standard Coho Annual 0.80 Lincoln 2005-2006 Spawning Surveys Basin Subbasin Reach ID Seg. Survey Name Type Species Status Year(s) Surv. Miles Siletz River Mainstem 25168.00 2 Fourth Of July Cr Random Coho Repeat 94,99,05 1.00 Siletz River Mainstem 25168.00 2 Fourth Of July Cr Random Steelhead 06 1.00 Siletz River Mainstem 25168.00 2 Fourth Of July Cr Random Fall Chinook 05 1.00 Siletz River Rock Creek 25134.00 1 Big Rock Cr Standard Fall Chinook Annual 0.75 Siletz River Schooner Creek 25256.70 1 Schooner Cr, N Fk Random Coho New 05 0.20 Spencer Creek Mainstem,N Fk,S Fk 25061.00 2 Spencer Creek, S. Fk. Random Coho Repeat 04,05 0.59 Spencer Creek Mainstem,N Fk,S Fk 25061.00 2 Spencer Creek, S. Fk. Random Steelhead 05,06 0.59 Yaquina River Mainstem And Bay 24944.00 3 Beaver Cr (Yaquina) Supplemental Coho 99,01,03,04,05 1.00 Yaquina River Mainstem And Bay 24953.30 1 Mill Cr, Trib A (Slack Cr) Supplemental Chum 94,95,96,97,98,99,00,01, 0.80 Yaquina River Mainstem And Bay 24953.70 1 Mill Creek Supplemental Chum 94,95,96,97,98,99,00,01, 0.70 Yaquina River Mainstem And Bay 24953.70 2 Upper Mill Creek Supplemental Chum 94,95,96,97,98,99,00,01, 1.26 Yaquina River Mainstem And Bay 24997.00 1 Simpson Creek Standard Chum 05 1.50 Yaquina River Mainstem And Bay 24998.00 1 Klamath Cr Random Coho Repeat 90,91,05 1.30 Yaquina River Mainstem And Bay 24998.00 1 Klamath Cr Random Steelhead 06 1.30 Yaquina River Mainstem And Bay 25046.00 2 Yaquina R, Spilde Cr To Little Standard Fall Chinook Annual 2.00 Yaquina Yaquina River Mainstem And Bay 25046.00 2 Yaquina R, Spilde Cr To Little Standard Coho Annual 2.00 Yaquina Yaquina River Mainstem And Bay 25046.00 2 Yaquina R, Spilde Cr To Little Random Coho Repeat 99,02,04,05 2.00 Yaquina Yaquina River Elk Creek 24958.00 1 Bear Cr Random Coho Repeat 99,02,05 1.00 Yaquina River Elk Creek 24958.00 1 Bear Cr Random Steelhead 03,05,06 1.00 Yaquina River Elk Creek 24963.70 1 Cougar Cr Random Coho Repeat 98,05 1.78 Yaquina River Elk Creek 24976.00 1.1 Spout Cr Random Coho Repeat 05 0.60 Yaquina River Elk Creek 24976.00 1.1 Spout Cr Random Steelhead 06 0.60 Yaquina River Elk Creek 24980.00 1 Spout Cr Random Coho Repeat 92,95,05 1.26 Yaquina River Elk Creek 24980.00 1 Spout Cr Random Steelhead 06 1.26 Yaquina River Little Elk Creek 25022.00 1 Salmon Cr Standard Fall Chinook Annual 0.60 Yaquina River Little Elk Creek 25022.00 1 Salmon Cr Standard Coho Annual 0.60 Yaquina River Little Elk Creek 25024.70 1 Oglesby Cr Random Coho Repeat 98,99,00,01,02,03,04,05 0.60 Yaquina River Little Elk Creek 25024.70 1 Oglesby Cr Random Steelhead 03,05,06 0.60 Beaver Creek Mainstem 24909.00 2 Tracy Cr Random Coho Pending 05 Beaver Creek Mainstem 24909.00 2 Tracy Cr Random Steelhead 06 Beaver Creek Mainstem 24919.00 2 Elkhorn Cr Random Coho Repeat 92,98,99,00,01,02,03,04, 0.98 Beaver Creek South Fork 24913.00 3 Beaver Cr, S Fk Supplemental Coho 99,01,03,04,05 0.88 Beaver Creek North Fork 24924.00 3 Beaver Cr, N Fk Random Coho New 05 0.60 Beaver Creek North Fork 24924.00 3 Beaver Cr, N Fk Random Steelhead 06 0.60 Lincoln 2005-2006 Spawning Surveys Basin Subbasin Reach ID Seg. Survey Name Type Species Status Year(s) Surv. Miles Beaver Creek North Fork 24924.00 3.1 Beaver Cr, N Fk, Peterson Cr Standard Coho Annual 1.22 To Lewis Cr Beaver Creek North Fork 24924.70 2 Beaver Cr, N Fk, Lewis Cr To Random Coho Repeat 93,96,98,99,02,05 0.96 Trib G Beaver Creek North Fork 24924.70 2 Beaver Cr, N Fk, Lewis Cr To Random Steelhead 06 0.96 Trib G Beaver Creek North Fork 24924.80 1 Beaver Cr, N Fk, Trib G Random Coho Repeat 98,99,00,01,02,03,04,05 1.37 Beaver Creek North Fork 24924.90 1 Beaver Cr, N Fk, Trib G to Trib H Supplemental Coho 02,03,04,05 0.40 Alsea River Mainstem And Bay 24670.00 2 Bear Cr Random Coho Repeat 98,99,00,01,02,03,04,05 1.14 Alsea River Mainstem And Bay 24691.00 1 Scott Cr Random Coho Repeat 98,99,05 1.13 Alsea River Mainstem And Bay 24691.00 1 Scott Cr Random Steelhead 06 1.13 Alsea River Drift Creek 24641.00 4 Lower Drift Creek Standard Fall Chinook Annual 1.50 Alsea River Drift Creek 24645.00 1 Flynn Cr Random Coho Repeat 97,99,00,02,05 1.31 Alsea River Drift Creek 24645.00 3 Flynn Cr Random Coho New 05 0.30 Alsea River Drift Creek 24645.00 3 Flynn Cr Random Steelhead 06 0.30 Alsea River Drift Creek 24646.00 2 Horse Cr Standard Coho Annual 1.00 Alsea River Drift Creek 24651.40 3 Gopher Cr Random Coho New 05 0.90 Alsea River Drift Creek 24651.40 3 Gopher Cr Random Steelhead 06 0.90 Alsea River Drift Creek 24652.00 1 Nettle Creek Standard Coho Annual 0.80 Alsea River Five Rivers 24708.00 2 Bear Cr Random Coho Repeat 98,05 1.49 Alsea River Five Rivers 24729.00 2 Little Lobster Cr Random Coho New 05 1.00 Alsea River Five Rivers 24729.00 2 Little Lobster Cr Random Steelhead 06 1.00 Alsea River Five Rivers 24730.00 1 (Lower) Lobster Creek Standard Fall Chinook Annual 2.20 Alsea River Five Rivers 24733.00 1 Preacher Cr Random Coho Repeat 96,97,05 1.05 Alsea River Five Rivers 24733.00 1 Preacher Cr Random Steelhead 06 1.05 Alsea River Five Rivers 24733.40 1 Preacher Cr Random Coho New 05 0.30 Alsea River Five Rivers 24733.40 1 Preacher Cr Random Steelhead 06 0.30 Alsea River Five Rivers 24744.00 2 Lobster Creek (Upper) Standard Coho Annual 1.30 Alsea River Five Rivers 24744.00 2 Lobster Creek (Upper) Random Coho Repeat 01,05 1.30 Alsea River Five Rivers 24745.00 2 S. Fk. (Upper) Lobster Creek Supplemental Coho 95,96,99,00,01,02,03,04, 1.76 Alsea River Five Rivers 24745.00 3 Lobster Cr, S Fk Supplemental Coho 94,95,96,99,00,01,02,03, 0.89 Alsea River Five Rivers 24746.00 2 East Fork Lobster Creek Supplemental Coho 95,96,99,00,01,02,03,04, 1.00 Alsea River Five Rivers 24754.00 1 Cherry Cr Standard Coho Annual 0.76 Alsea River Five Rivers 24758.00 1 Buck Cr Random Coho Repeat 90,05 0.50 Alsea River Five Rivers 24758.00 1.1 Buck Creek Standard Fall Chinook Annual 1.00 Alsea River Five Rivers 24766.00 1 Crab Cr Random Coho Repeat 94,96,99,02,05 0.94 Alsea River Five Rivers 24770.00 1 Crazy Cr Random Coho Repeat 05 0.84 Lincoln 2005-2006 Spawning Surveys Basin Subbasin Reach ID Seg. Survey Name Type Species Status Year(s) Surv. Miles Alsea River Five Rivers 24770.00 1 Crazy Cr Random Steelhead 06 0.84 Alsea River North Fork 24835.00 1 North Fork Alsea River Standard Fall Chinook Annual 2.30 Alsea River North Fork 24847.00 1 Baker Cr Random Coho Pending 05 Alsea River North Fork 24850.00 1 Crooked Cr Random Coho Repeat 98,99,00,01,02,03,04,05 1.14 Alsea River South Fork 24882.80 1 Swamp Cr Random Coho Repeat 98,99,00,01,02,03,04,05 0.92 Alsea River South Fork 24882.80 1 Swamp Cr Random Steelhead 03,04,05,06 0.92 Alsea River South Fork 24882.80 2 Swamp Cr Random Coho New 05 0.80 Alsea River South Fork 24887.00 2 Tobe Cr Random Coho Repeat 96,05 1.18 Siuslaw 2005-2006 Spawning Surveys Basin Subbasin Reach ID Seg. Survey Name Type Species Status Year(s) Surv. Miles Yachats River Mainstem 24561.00 1 Marks Cr Random Coho Repeat 91,99,02,05 0.60 Yachats River Mainstem 24573.00 2 Axtel Cr Random Coho Repeat 93,97,04,05 0.66 Yachats River Mainstem 24588.00 1 Yachats R Neiglick to Stump Random Coho Repeat 98,99,02,05 0.88 Yachats River Mainstem 24588.00 1 Yachats R Neiglick to Stump Random Steelhead 03,04,06 0.88 Yachats River Mainstem 24593.00 2 Yachats R, School Fork Standard Coho Annual 0.70 Yachats River Mainstem 24595.00 1 Grass Cr Random Coho Repeat 95,05 0.96 Yachats River Mainstem 24595.00 1 Grass Cr Random Steelhead 06 0.96 Yachats River Mainstem 24596.00 2 Yachats R, Grass Cr To Random Coho Repeat 03,05 1.30 Headwaters Yachats River Mainstem 24596.00 2 Yachats R, Grass Cr To Random Steelhead 04,06 1.30 Headwaters Yachats River North Fork 24578.00 1 Williamson Cr Standard Coho Annual 1.30 Cummins Cr Mainstem 24544.00 2 Cummins Cr Random Coho Repeat 96,98,99,00,01,02,03,04, 1.23 Cummins Cr Mainstem 24544.00 2 Cummins Cr Random Steelhead 05,06 1.23 Bob Creek Mainstem 24540.00 1 Bob Cr Random Coho Repeat 93,95,05 1.10 Tenmile Creek Mainstem 24528.00 2 Tenmile Cr Random Coho New 05 1.10 Tenmile Creek Mainstem 24531.00 1 Tenmile Cr, S Fk Random Coho Repeat 95,05 0.48 Tenmile Creek Mainstem 24531.00 1 Tenmile Cr, S Fk Random Steelhead 06 0.48 Big Creek Mainstem & S Fk 24518.00 1 Big Cr Random Coho Repeat 91,04,05 1.10 Big Creek Mainstem & S Fk 24518.00 1 Big Cr Random Steelhead 06 1.10 Cape Creek Mainstem 24498.00 1 Cape Cr Random Coho Repeat 91,01,03,05 1.50 Cape Creek Mainstem 24498.00 1 Cape Cr Random Steelhead 04,06 1.50 Siuslaw River Mainstem 24046.00 1 Lawson Cr Random Coho Repeat 99,02,05 1.14 Siuslaw River Mainstem 24046.00 1 Lawson Cr Random Steelhead 03,06 1.14 Siuslaw River Mainstem 24054.00 1 Divide (David) Cr Random Coho Repeat 90,91,05 1.25 Siuslaw River Mainstem 24058.00 2 Sweet Creek Standard Fall Chinook Annual 0.50 Siuslaw River Mainstem 24084.00 3 Hadsall Cr Random Coho Repeat 05 1.45 Siuslaw River Mainstem 24084.00 3 Hadsall Cr Random Steelhead 06 1.45 Siuslaw River Mainstem 24086.00 1 Hollenbeck Cr Random Coho Repeat 93,98,99,00,01,02,03,04, 0.36 Siuslaw River Mainstem 24086.00 1 Hollenbeck Cr Random Steelhead 03,04,05,06 0.36 Siuslaw River Mainstem 24238.00 1 Brush Cr, E Fk Random Coho New 05 0.50 Siuslaw River Mainstem 24238.00 1 Brush Cr, E Fk Random Steelhead 06 0.50 Siuslaw River Mainstem 24261.00 1 Waite Cr Random Coho Repeat 92,05 1.01 Siuslaw River Mainstem 24261.00 1 Waite Cr Random Steelhead 06 1.01 Siuslaw River Mainstem 24288.10 1 Knapp Cr Random Coho Repeat 98,99,00,01,02,03,04,05 0.89 Siuslaw River Mainstem 24288.10 1 Knapp Cr Random Steelhead 03,04,05,06 0.89 Siuslaw 2005-2006 Spawning Surveys Basin Subbasin Reach ID Seg. Survey Name Type Species Status Year(s) Surv. Miles Siuslaw River Mainstem 24288.90 1 Miller Cr Random Coho New 05 0.70 Siuslaw River Mainstem 24301.00 2 Whittaker Creek (Lower) Standard Fall Chinook Annual 0.30 Siuslaw River Mainstem 24303.00 2 Whittaker Creek (Upper) Standard Fall Chinook Annual 0.40 Siuslaw River Mainstem 24347.00 1 (Not) Big Canyon Creek Random Coho Repeat 02,05 0.72 Siuslaw River Mainstem 24349.00 1.1 Esmond Cr Standard Fall Chinook Annual 1.00 Siuslaw River Mainstem 24358.00 1 Esmond Cr Trib A Random Coho Repeat 91,05 0.43 Siuslaw River Mainstem 24363.20 2 Pugh Cr Random Coho Repeat 96,05 0.88 Siuslaw River Mainstem 24373.00 1 Clay Cr Random Coho Repeat 99,00,01,02,03,04,05 1.15 Siuslaw River Mainstem 24373.00 1 Clay Cr Random Steelhead 03,04,05,06 1.15 Siuslaw River Mainstem 24373.00 2 Clay Cr Random Coho New 05 0.90 Siuslaw River Mainstem 24373.00 2 Clay Cr Random Steelhead 06 0.90 Siuslaw River Mainstem 24391.00 1 Bear Cr Random Coho Repeat 99,02,05 0.86 Siuslaw River Mainstem 24391.00 1 Bear Cr Random Steelhead 03,06 0.86 Siuslaw River Mainstem 24393.00 1 Bear Creek Random Coho Repeat 03,05 0.30 Siuslaw River Mainstem 24409.00 1 Jeans Cr Random Coho New 05 0.70 Siuslaw River Mainstem 24415.00 2 Bottle Cr (Middle) Random Coho Repeat 92,97,05 0.91 Siuslaw River Mainstem 24421.00 1 Buck Cr, (B To D) Random Coho Repeat 97,98,99,00,01,02,03,04, 1.07 Siuslaw River Mainstem 24425.00 1 Russel Cr (Mouth/Trib A) Random Coho Repeat 98,99,00,01,02,03,04,05 0.89 Siuslaw River Mainstem 24425.00 1 Russel Cr (Mouth/Trib A) Random Steelhead 03,04,05,06 0.89 Siuslaw River Mainstem 24439.00 1 Letz Cr Random Coho Repeat 95,05 1.56 Siuslaw River North Fork 24018.00 2 Uncle Cr Random Coho Repeat 02,05 0.29 Siuslaw River North Fork 24018.00 2 Uncle Cr Random Steelhead 03,06 0.29 Siuslaw River North Fork 24019.40 1 Condon Cr Random Coho Repeat 97,99,00,02,05 1.54 Siuslaw River North Fork 24019.40 1 Condon Cr Random Steelhead 03,06 1.54 Siuslaw River North Fork 24024.60 1 Mcleod Cr Random Coho New 05 0.60 Siuslaw River North Fork 24024.60 1 Mcleod Cr Random Steelhead 06 0.60 Siuslaw River North Fork 24025.00 3 Mcleod Cr Random Coho Repeat 95,99,02,05 1.42 Siuslaw River North Fork 24026.00 2 North Fork Siuslaw R Standard Fall Chinook Annual 0.80 Siuslaw River North Fork 24028.00 3 Siuslaw R, N Fk Random Coho New 05 0.90 Siuslaw River North Fork 24033.70 1 Porter Cr Random Coho New 05 1.20 Siuslaw River Lake Creek 24128.00 2 Elk Cr Random Coho Repeat 95,05 0.99 Siuslaw River Lake Creek 24128.00 2 Elk Cr Random Steelhead 06 0.99 Siuslaw River Lake Creek 24135.00 1 Rogers Cr Standard Fall Chinook Annual 1.30 Siuslaw River Lake Creek 24135.00 1 Rogers Cr Standard Coho Annual 1.30 Siuslaw River Lake Creek 24135.00 1 Rogers Cr Random Coho Repeat 95,97,98,99,00,01,02,03, 1.30 Siuslaw River Lake Creek 24135.00 1 Rogers Cr Random Steelhead 03,04,05,06 1.30 Siuslaw 2005-2006 Spawning Surveys Basin Subbasin Reach ID Seg. Survey Name Type Species Status Year(s) Surv. Miles Siuslaw River Lake Creek 24135.00 1 Rogers Cr Random Fall Chinook 02,03,04,05 1.30 Siuslaw River Lake Creek 24136.00 1 West Fk. Indian Creek Standard Fall Chinook Annual 1.20 Siuslaw River Lake Creek 24138.00 1 West Fork Indian (Pyle To Random Coho Repeat 05 1.20 Maria) Siuslaw River Lake Creek 24138.00 1 West Fork Indian (Pyle To Random Fall Chinook 05 1.20 Maria) Siuslaw River Lake Creek 24144.00 1 Gibson Cr Random Coho Repeat 99,02,05 0.73 Siuslaw River Lake Creek 24145.00 1 Indian Cr Random Coho Repeat 91,05 0.90 Siuslaw River Lake Creek 24145.00 1 Indian Cr Random Steelhead 06 0.90 Siuslaw River Lake Creek 24145.00 1 Indian Cr Random Fall Chinook 05 0.90 Siuslaw River Lake Creek 24145.00 2 Indian Cr Random Coho Repeat 90,94,03,05 1.10 Siuslaw River Lake Creek 24145.00 2 Indian Cr Random Steelhead 04,06 1.10 Siuslaw River Lake Creek 24145.00 2 Indian Cr Random Fall Chinook 03,04,05 1.10 Siuslaw River Lake Creek 24146.70 1 Taylor Cr Random Coho New 05 0.20 Siuslaw River Lake Creek 24146.70 1 Taylor Cr Random Steelhead 06 0.20 Siuslaw River Lake Creek 24149.50 1 Indian Cr, N Fk Random Coho Repeat 97,00,05 1.10 Siuslaw River Lake Creek 24149.60 1 Indian Cr, N Fk, Trib D Random Coho Repeat 05 0.90 Siuslaw River Lake Creek 24151.00 3 Green Cr Random Coho Repeat 96,98,99,00,01,02,03,04, 1.06 Siuslaw River Lake Creek 24151.00 3 Green Cr Random Fall Chinook 02,03,04,05 1.06 Siuslaw River Lake Creek 24159.00 1 Misery Cr Random Coho Repeat 93,98,99,00,01,02,03,04, 1.00 Siuslaw River Lake Creek 24159.00 1 Misery Cr Random Steelhead 03,04,05,06 1.00 Siuslaw River Lake Creek 24159.00 1 Misery Cr Random Fall Chinook 02,03,04,05 1.00 Siuslaw River Lake Creek 24170.00 1 Rock Cr Random Coho Repeat 90,94,95,96,05 0.87 Siuslaw River Lake Creek 24170.00 1 Rock Cr Random Steelhead 06 0.87 Siuslaw River Lake Creek 24170.00 1 Rock Cr Random Fall Chinook 05 0.87 Siuslaw River Lake Creek 24172.00 2 Buck Cr Random Coho New 05 0.80 Siuslaw River Lake Creek 24172.00 2 Buck Cr Random Fall Chinook 05 0.80 Siuslaw River Lake Creek 24181.30 2 Fawn Cr Random Coho Repeat 94,05 0.96 Siuslaw River Lake Creek 24181.30 2 Fawn Cr Random Steelhead 06 0.96 Siuslaw River Lake Creek 24189.00 2 Chappell Cr Random Coho Repeat 99,02,05 0.59 Siuslaw River Lake Creek 24189.00 2 Chappell Cr Random Steelhead 03,06 0.59 Siuslaw River Lake Creek 24205.00 1 Lamb Cr Random Coho Repeat 96,05 0.81 Siuslaw River Lake Creek 24206.00 2 Lake Creek Standard Fall Chinook Annual 0.80 Siuslaw River Lake Creek 24232.00 1 Pucker Cr Random Coho Repeat 00,01,02,03,04,05 0.94 Siuslaw River Lake Creek 24232.00 1 Pucker Cr Random Steelhead 03,04,05,06 0.94 Siuslaw River Wolf Creek 24338.00 1 Panther Cr Random Coho New 05 0.70 Siuslaw 2005-2006 Spawning Surveys Basin Subbasin Reach ID Seg. Survey Name Type Species Status Year(s) Surv. Miles Siuslaw River Wolf Creek 24345.70 1 Wolf Cr Random Coho New 05 0.50 Siuslaw River Wolf Creek 24345.70 1 Wolf Cr Random Steelhead 06 0.50 Siltcoos River Maple Creek 23995.00 1 Henderson Creek Lake Coho Annual 99no, 00no, 01no 0.30 Siltcoos River Maple Creek 23997.00 1 North Prong Creek Lake Coho Annual 99no, 00no, 01no 0.50 Siltcoos River Maple Creek 23998.00 1 Maple Creek Lake Coho Annual 99no, 00no, 01no 0.80 Siltcoos River Fiddle Creek 23965.00 2 Alder Creek Lake Coho Annual 1.00 Siltcoos River Fiddle Creek 23968.00 1 Bear Cr. Random Coho Repeat 98,00,01,02,03,04,05 0.97 Siltcoos River Fiddle Creek 23974.40 4 Fiddle Creek Lake Coho Annual 1.50 Tahkenitch Creek Fivemile Creek 23956.00 1 Bell Cr Random Coho Repeat 99,00,02,05 1.03 Tahkenitch Creek Fivemile Creek 23957.00 2 Fivemile Creek Lake Coho Annual 0.80 Tahkenitch Creek Leitel Creek 23949.00 3 Leitel Creek Lake Coho Annual 0.80 Umpqua 2005-2006 Spawning Surveys Basin Subbasin Reach ID Seg. Survey Name Type Species Status Year(s) Surv. Miles Umpqua River Mainstem And Bay 22401.00 1 Dry Cr Random Coho Repeat 92,98,99,00,01,02,03,04, 0.89 Umpqua River Mainstem And Bay 22401.00 1 Dry Cr Random Steelhead 03,06 0.89 Umpqua River Mainstem And Bay 22403.00 2 Miller Cr Random Coho New 05 0.80 Umpqua River Mainstem And Bay 22403.00 2 Miller Cr Random Steelhead 06 0.80 Umpqua River Mainstem And Bay 22624.00 3 Dean Cr (Sheps/D-Upper) Random Coho Repeat 94,05 0.69 Umpqua River Mainstem And Bay 22642.00 1 Charlotte Cr Random Coho Repeat 93,99,01,02,05 1.02 Umpqua River Mainstem And Bay 22642.00 1 Charlotte Cr Random Steelhead 03,06 1.02 Umpqua River Mainstem And Bay 22644.00 1 Luder Cr Random Coho New 05 0.60 Umpqua River Mainstem And Bay 22653.00 4 Camp Cr Random Coho Repeat 98,99,00,01,02,03,04,05 1.24 Umpqua River Mainstem And Bay 22654.00 1 Buck Cr Random Coho New 05 0.60 Umpqua River Mainstem And Bay 22654.30 1 Buck Cr, Trib. A Random Coho New 05 0.50 Umpqua River Mainstem And Bay 22655.00 1 Camp Cr Random Coho New 05 0.95 Umpqua River Mainstem And Bay 22655.00 1 Camp Cr Random Steelhead 06 0.95 Umpqua River Mainstem And Bay 22655.00 2 Camp Cr Random Coho Repeat 99,01,02,05 1.14 Umpqua River Mainstem And Bay 22676.00 1 Little Mill Cr Random Coho New 05 1.30 Umpqua River Mainstem And Bay 22676.00 1 Little Mill Cr Random Steelhead 06 1.30 Umpqua River Mainstem And Bay 22683.00 1 Purdy Cr Random Coho Repeat 93,05 0.23 Umpqua River Mainstem And Bay 22683.00 1 Purdy Cr Random Steelhead 06 0.23 Umpqua River Mainstem And Bay 22686.00 2 Weatherly Cr Random Coho Repeat 97,99,02,05 0.98 Umpqua River Mainstem And Bay 22686.00 2 Weatherly Cr Random Steelhead 03,06 0.98 Umpqua River Mainstem And Bay 22686.90 2 Weatherly Cr Random Coho New 05 1.20 Umpqua River Mainstem And Bay 22688.00 3 Lutsinger Cr Random Coho Repeat 98,99,00,01,02,03,04,05 0.95 Umpqua River Mainstem And Bay 22688.00 3 Lutsinger Cr Random Steelhead 03,06 0.95 Umpqua River Mainstem And Bay 22695.00 1 Little Paradise Cr Random Coho Repeat 91,01,05 0.95 Umpqua River Mainstem And Bay 22695.00 1 Little Paradise Cr Random Steelhead 06 0.95 Umpqua River Mainstem And Bay 22828.60 1 Brads Cr, Trib A Random Coho New 05 0.60 Umpqua River Mainstem And Bay 22828.60 1 Brads Cr, Trib A Random Steelhead 06 0.60 Umpqua River Mainstem And Bay 22836.80 1 Yellow Cr Random Coho New 05 0.30 Umpqua River Mainstem And Bay 22844.30 1 Little Canyon Cr, Trib A Random Coho New 05 0.70 Umpqua River Mainstem And Bay 22844.30 1 Little Canyon Cr, Trib A Random Steelhead 06 0.70 Umpqua River Mainstem And Bay 22857.90 1 Little Wolf Cr Random Coho New 05 1.10 Umpqua River Mainstem And Bay 22861.60 1 Whiskey Camp Cr Random Coho New 05 0.50 Umpqua River Mainstem And Bay 22862.00 1 Wolf Cr Random Coho Repeat 98,99,00,01,02,03,04,05 1.03 Umpqua River Mainstem And Bay 22870.00 2 Hubbard Cr Random Coho Repeat 96,05 1.11 Umpqua River Mainstem And Bay 22870.00 2 Hubbard Cr Random Steelhead 06 1.11 Umpqua River Mainstem And Bay 22875.00 1 Bear Creek Random Coho Repeat 03,05 0.50 Umpqua 2005-2006 Spawning Surveys Basin Subbasin Reach ID Seg. Survey Name Type Species Status Year(s) Surv. Miles Umpqua River Mainstem And Bay 22876.00 1 Hubbard Cr. Random Coho Repeat 98,99,00,01,02,03,04,05 0.92 Umpqua River Mainstem And Bay 22878.00 1 Hubbard Cr (Rock To Camp) Random Coho Repeat 99,00,02,03,05 0.84 Umpqua River Mainstem And Bay 22878.00 1 Hubbard Cr (Rock To Camp) Random Steelhead 03,06 0.84 Umpqua River Smith River 22418.00 1 Otter Cr, N Fk Random Coho Repeat 02,05 1.46 Umpqua River Smith River 22418.00 1 Otter Cr, N Fk Random Steelhead 06 1.46 Umpqua River Smith River 22442.00 1 Railroad Cr Random Coho Repeat 99,02,05 1.03 Umpqua River Smith River 22442.00 1 Railroad Cr Random Steelhead 03,06 1.03 Umpqua River Smith River 22442.00 2 Railroad Cr Random Coho Repeat 97,05 0.78 Umpqua River Smith River 22442.00 2 Railroad Cr Random Steelhead 06 0.78 Umpqua River Smith River 22450.00 1 Hell Of Bush Cr Random Coho Repeat 94,99,05 0.98 Umpqua River Smith River 22450.00 1 Hell Of Bush Cr Random Steelhead 06 0.98 Umpqua River Smith River 22456.00 2 Moore Cr Random Coho New 05 0.30 Umpqua River Smith River 22462.70 1 Smith R, N Fk, W Br Random Coho Repeat 99,02,05 0.44 Umpqua River Smith River 22466.80 1 Cedar Cr Random Coho New 05 0.80 Umpqua River Smith River 22466.80 1 Cedar Cr Random Steelhead 06 0.80 Umpqua River Smith River 22467.70 1 Smith R, N Fk Random Coho New 05 1.60 Umpqua River Smith River 22467.70 1 Smith R, N Fk Random Steelhead 06 1.60 Umpqua River Smith River 22468.76 1 M Fk Of N Fk Smith R Random Coho New 05 0.90 Umpqua River Smith River 22468.76 1 M Fk Of N Fk Smith R Random Steelhead 06 0.90 Umpqua River Smith River 22469.00 2 Smith R, N Fk Random Coho New 05 0.80 Umpqua River Smith River 22469.00 2 Smith R, N Fk Random Steelhead 06 0.80 Umpqua River Smith River 22485.00 3 Spencer Cr Random Coho Repeat 97,05 1.44 Umpqua River Smith River 22485.00 3 Spencer Cr Random Steelhead 06 1.44 Umpqua River Smith River 22501.50 1 Smith R, W Fk,Trib B To Crane Random Coho Repeat 05 1.11 Cr Umpqua River Smith River 22504.00 2 Beaver Cr Standard Coho Annual 1.50 Umpqua River Smith River 22507.00 4 Smith River, W FK Gold Cr To Random Coho Repeat 05 1.03 Headwaters Umpqua River Smith River 22507.60 1 Smith R, W Fk, Trib G Random Coho New 05 1.50 Umpqua River Smith River 22507.60 1 Smith R, W Fk, Trib G Random Steelhead 06 1.50 Umpqua River Smith River 22511.00 3 Blackwell Cr Random Coho New 05 0.40 Umpqua River Smith River 22517.00 1 Beaver Cr Random Coho Repeat 98,99,00,01,02,03,04,05 0.50 Umpqua River Smith River 22517.00 1 Beaver Cr Random Steelhead 00,01,02,03,06 0.50 Umpqua River Smith River 22517.30 1 Beaver Cr, Trib A Random Coho New 05 0.20 Umpqua River Smith River 22517.30 1 Beaver Cr, Trib A Random Steelhead 06 0.20 Umpqua River Smith River 22521.00 3 S. Sister Cr, Mouth To Jeff Cr Random Coho Repeat 97,99,00,02,03,05 1.24 Umpqua 2005-2006 Spawning Surveys Basin Subbasin Reach ID Seg. Survey Name Type Species Status Year(s) Surv. Miles Umpqua River Smith River 22528.00 1 N Sister Cr Random Coho Repeat 93,05 0.42 Umpqua River Smith River 22528.00 1 N Sister Cr Random Steelhead 06 0.42 Umpqua River Smith River 22530.00 1 N Sister Cr, Sweden Cr To Trib Random Coho Repeat 98,99,00,01,02,03,04,05 0.90 A Umpqua River Smith River 22530.00 1 N Sister Cr, Sweden Cr To Trib Random Steelhead 00,01,02,03,04,05,06 0.90 A Umpqua River Smith River 22537.00 1 Marsh Cr Random Coho Repeat 93,98,99,00,01,02,03,04, 0.43 Umpqua River Smith River 22537.00 1 Marsh Cr Random Steelhead 00,01,02,03,06 0.43 Umpqua River Smith River 22546.30 1 Mosetown Cr, E Fk, Trib A Random Coho Repeat 98,99,01,02,03,04,05 0.86 Umpqua River Smith River 22546.30 1 Mosetown Cr, E Fk, Trib A Random Steelhead 00,01,02,03,06 0.86 Umpqua River Smith River 22548.70 1 Smith R, Trib X To Halfway Cr Random Coho Repeat 05 1.00 seg 1 Umpqua River Smith River 22548.70 1 Smith R, Trib X To Halfway Cr Random Steelhead 01,06 1.00 seg 1 Umpqua River Smith River 22549.70 3 Halfway Cr Random Coho New 05 1.10 Umpqua River Smith River 22549.90 1 Halfway Cr Random Coho New 05 0.80 Umpqua River Smith River 22564.30 1 Hardenbrook Cr Random Coho Repeat 00,05 1.40 Umpqua River Smith River 22577.00 2 Panther Cr, Mouth To Trib A Random Coho Repeat 98,99,00,01,02,03,04,05 1.24 Umpqua River Smith River 22584.00 1 Smith R, Little S Fk, Mouth To Random Coho Repeat 91,99,00,01,02,04,05 0.96 Trib 1 Umpqua River Smith River 22584.00 1 Smith R, Little S Fk, Mouth To Random Steelhead 00,01,02,03,06 0.96 Trib 1 Umpqua River Smith River 22585.00 4 Smith R, S Fk Random Coho Repeat 01,05 0.97 Umpqua River Smith River 22585.00 4 Smith R, S Fk Random Steelhead 02,06 0.97 Umpqua River Elk Creek 22713.70 1 Big Tom Folley Cr Random Coho Repeat 04,05 0.80 Umpqua River Elk Creek 22713.70 1 Big Tom Folley Cr Random Steelhead 05,06 0.80 Umpqua River Elk Creek 22721.00 2 Brush Creek Random Coho Repeat 99,02,03,05 1.14 Umpqua River Elk Creek 22735.00 1 Hardscrabble Cr Random Coho Repeat 98,99,00,01,02,03,04,05 1.10 Umpqua River Elk Creek 22756.00 1 Sand Cr Random Coho Repeat 98,99,00,01,02,03,04,05 1.37 Umpqua River Elk Creek 22756.00 1 Sand Cr Random Steelhead 03,06 1.37 Umpqua River Elk Creek 22760.72 1 Sand Cr, Trib A Random Coho New 05 0.30 Umpqua River Elk Creek 22760.74 1 Sand Cr Random Coho Repeat 00,03,05 0.70 Umpqua River Elk Creek 22760.74 1 Sand Cr Random Steelhead 06 0.70 Umpqua River Elk Creek 22762.00 5 Rock Cr Random Coho New 05 0.60 Umpqua River Elk Creek 22773.00 2 Yoncalla Cr Random Coho New 05 0.70 Umpqua River Elk Creek 22807.00 1 Curtis Cr Random Coho Repeat 98,99,00,01,02,03,04,05 1.40 Umpqua River Elk Creek 22807.00 1 Curtis Cr Random Steelhead 03,06 1.40 Umpqua River Elk Creek 22810.00 2 Elk Cr Random Coho Repeat 04,05 0.50 Umpqua 2005-2006 Spawning Surveys Basin Subbasin Reach ID Seg. Survey Name Type Species Status Year(s) Surv. Miles Umpqua River Elk Creek 22810.00 2 Elk Cr Random Steelhead 05,06 0.50 Umpqua River Elk Creek 22811.00 3 Adams Cr Random Coho Repeat 99,01,02,05 1.13 Umpqua River Elk Creek 22811.00 3 Adams Cr Random Steelhead 03,06 1.13 Umpqua River Elk Creek 22816.80 1 Elk Cr Random Coho Repeat 00,05 1.35 Umpqua River North Umpqua 23622.00 2 Sutherlin Cr Random Coho New 05 1.30 Umpqua River North Umpqua 23622.00 2 Sutherlin Cr Random Steelhead 06 1.30 Umpqua River North Umpqua 23626.00 2 Sutherlin Cr Random Coho New 05 1.20 Umpqua River North Umpqua 23630.00 2 Clover Cr Random Coho New 05 0.90 Umpqua River North Umpqua 23630.00 2 Clover Cr Random Steelhead 06 0.90 Umpqua River North Umpqua 23649.00 3 Cavitt Cr Random Coho New 05 0.90 Umpqua River North Umpqua 23649.00 3 Cavitt Cr Random Steelhead 06 0.90 Umpqua River North Umpqua 23661.00 1 Cavitt Cr Random Coho New 05 1.10 Umpqua River North Umpqua 23676.00 1 Little River Random Coho New 05 1.30 Umpqua River North Umpqua 23676.00 1 Little River Random Steelhead 06 1.30 Umpqua River North Umpqua 23690.00 1 Little R Random Coho New 05 1.20 Umpqua River North Umpqua 23728.00 1 Rock Cr Random Coho Repeat 05 1.70 Umpqua River North Umpqua 23740.70 1 Rock Cr Random Coho New 05 0.20 Umpqua River North Umpqua 23743.00 3 Rock Cr, E Fk Random Coho New 05 0.60 Umpqua River North Umpqua 23743.00 3 Rock Cr, E Fk Random Steelhead 06 0.60 Umpqua River North Umpqua 23746.00 3 Rock Cr Random Coho New 05 1.30 Umpqua River North Umpqua 23746.00 3 Rock Cr Random Steelhead 06 1.30 Umpqua River North Umpqua 23748.00 1 Honey Cr Random Coho New 05 1.30 Umpqua River North Umpqua 23748.00 1 Honey Cr Random Steelhead 06 1.30 Umpqua River North Umpqua 23752.00 1 Susan Cr Random Coho New 05 0.60 Umpqua River North Umpqua 23767.00 2 Canton Cr Random Coho New 05 1.00 Umpqua River North Umpqua 23845.00 1 Panther Cr Random Coho New 05 0.70 Umpqua River South Umpqua 22976.00 1 Callahan Cr Random Coho Repeat 99,02,05 0.82 Umpqua River South Umpqua 22976.00 1 Callahan Cr Random Steelhead 03,06 0.82 Umpqua River South Umpqua 22989.70 1 Deer Cr Random Coho New 05 0.20 Umpqua River South Umpqua 22989.70 1 Deer Cr Random Steelhead 06 0.20 Umpqua River South Umpqua 22991.00 2 Deer Cr Random Coho New 05 1.30 Umpqua River South Umpqua 22992.00 1 Deer Cr, S Fk Random Coho New 05 1.00 Umpqua River South Umpqua 22992.00 1 Deer Cr, S Fk Random Steelhead 06 1.00 Umpqua River South Umpqua 22992.00 2 Deer Cr, S Fk Random Coho New 05 1.40 Umpqua River South Umpqua 22999.00 1 Deer Cr, N Fk Random Coho Repeat 97,98,99,00,02,03,04,05 0.49 Umpqua River South Umpqua 22999.00 1 Deer Cr, N Fk Random Steelhead 03,04,05,06 0.49 Umpqua 2005-2006 Spawning Surveys Basin Subbasin Reach ID Seg. Survey Name Type Species Status Year(s) Surv. Miles Umpqua River South Umpqua 22999.70 3 Deer Cr, N Fk Random Coho New 05 1.10 Umpqua River South Umpqua 23001.40 1 Roberts Creek Random Coho Repeat 03,05 1.90 Umpqua River South Umpqua 23001.40 1 Roberts Creek Random Steelhead 04,06 1.90 Umpqua River South Umpqua 23013.00 3 Tenmile Cr Random Coho New 05 1.00 Umpqua River South Umpqua 23013.00 3 Tenmile Cr Random Steelhead 06 1.00 Umpqua River South Umpqua 23015.00 1 Tenmile Cr Random Coho New 05 0.70 Umpqua River South Umpqua 23022.00 4 Olalla Cr Random Coho Repeat 91,92,05 1.10 Umpqua River South Umpqua 23034.00 1 Olalla Cr Random Coho Repeat 99,00,02,05 1.14 Umpqua River South Umpqua 23034.00 1 Olalla Cr Random Steelhead 03,06 1.14 Umpqua River South Umpqua 23041.00 3 Lookingglass Cr Random Coho Repeat 98,99,00,01,02,03,04,05 1.24 Umpqua River South Umpqua 23041.00 3 Lookingglass Cr Random Steelhead 03,04,05,06 1.24 Umpqua River South Umpqua 23042.00 2 Archambeau Cr Random Coho Repeat 99,02,05 0.71 Umpqua River South Umpqua 23042.00 2 Archambeau Cr Random Steelhead 03,06 0.71 Umpqua River South Umpqua 23063.40 1 Rice Cr Random Coho Repeat 00,02,03,04,05 1.24 Umpqua River South Umpqua 23063.40 1 Rice Cr Random Steelhead 03,06 1.24 Umpqua River South Umpqua 23069.00 2 S Umpqua R, Clark Br Random Coho Repeat 93,99,02,05 0.76 Umpqua River South Umpqua 23097.00 1 Lally Cr Random Coho Repeat 99,02,05 1.14 Umpqua River South Umpqua 23108.00 3 Bilger Cr Random Coho New 05 0.50 Umpqua River South Umpqua 23108.00 3 Bilger Cr Random Steelhead 06 0.50 Umpqua River South Umpqua 23117.00 3 Frozen Cr, Left Fk Random Coho Repeat 99,00,05 1.14 Umpqua River South Umpqua 23117.00 3 Frozen Cr, Left Fk Random Steelhead 06 1.14 Umpqua River South Umpqua 23121.00 1 Riser Cr Random Coho Repeat 98,99,00,01,02,03,04,05 0.77 Umpqua River South Umpqua 23121.00 1 Riser Cr Random Steelhead 03,06 0.77 Umpqua River South Umpqua 23122.00 1 Slide Cr Random Coho Repeat 98,99,01,02,04,05 1.29 Umpqua River South Umpqua 23122.00 1 Slide Cr Random Steelhead 03,06 1.29 Umpqua River South Umpqua 23144.00 2 Russell Cr Random Coho Repeat 05 0.53 Umpqua River South Umpqua 23144.00 2 Russell Cr Random Steelhead 06 0.53 Umpqua River South Umpqua 23166.00 1 Doe Cr Random Coho Repeat 96,97,98,99,00,01,02,03, 1.08 Umpqua River South Umpqua 23172.00 1 Iron Mtn Cr Random Coho Repeat 97,01,05 0.59 Umpqua River South Umpqua 23172.00 1 Iron Mtn Cr Random Steelhead 06 0.59 Umpqua River South Umpqua 23188.00 1 Cow Cr,W Fk (Mouth To Jacob) Random Coho Repeat 05 1.46 Umpqua River South Umpqua 23191.00 4 Bear Creek Random Coho Repeat 05 1.00 Umpqua River South Umpqua 23191.00 4 Bear Creek Random Steelhead 06 1.00 Umpqua River South Umpqua 23207.00 1 Bobby Cr Random Coho Repeat 97,05 0.20 Umpqua River South Umpqua 23207.00 1 Bobby Cr Random Steelhead 06 0.20 Umpqua River South Umpqua 23209.30 1 Elk Valley Cr, E Fk Random Coho Repeat 98,99,00,01,02,03,04,05 0.92 Umpqua 2005-2006 Spawning Surveys Basin Subbasin Reach ID Seg. Survey Name Type Species Status Year(s) Surv. Miles Umpqua River South Umpqua 23209.30 1 Elk Valley Cr, E Fk Random Steelhead 03,06 0.92 Umpqua River South Umpqua 23222.00 1 Cow Cr, W Fk Random Coho Repeat 98,99,00,01,02,03,04,05 0.97 Umpqua River South Umpqua 23222.00 1 Cow Cr, W Fk Random Steelhead 04,05,06 0.97 Umpqua River South Umpqua 23255.00 1 Middle Cr Random Coho Repeat 98,99,00,01,02,03,04,05 0.28 Umpqua River South Umpqua 23255.00 1 Middle Cr Random Steelhead 04,05,06 0.28 Umpqua River South Umpqua 23271.00 1 Riffle Cr Random Coho Repeat 99,02,05 1.26 Umpqua River South Umpqua 23271.00 1 Riffle Cr Random Steelhead 03,06 1.26 Umpqua River South Umpqua 23299.00 2 Wood Cr Random Coho Repeat 98,99,02,05 0.87 Umpqua River South Umpqua 23299.00 2 Wood Cr Random Steelhead 03,06 0.87 Umpqua River South Umpqua 23299.00 3 Wood Cr Random Coho New 05 0.70 Umpqua River South Umpqua 23304.00 1 Windy Creek Random Coho Repeat 01,02,05 1.35 Umpqua River South Umpqua 23304.00 1 Windy Creek Random Steelhead 06 1.35 Umpqua River South Umpqua 23308.00 1 Cow Cr, Fortune Br Random Coho Repeat 99,02,05 1.09 Umpqua River South Umpqua 23308.00 1 Cow Cr, Fortune Br Random Steelhead 03,06 1.09 Umpqua River South Umpqua 23313.00 1 Bull Run Cr Random Coho Repeat 97,98,99,00,01,02,03,04, 1.27 Umpqua River South Umpqua 23325.00 1 Cow Creek blue to wildcat Random Coho Repeat 05 1.00 Umpqua River South Umpqua 23325.00 1 Cow Creek blue to wildcat Random Steelhead 04,05,06 1.00 Umpqua River South Umpqua 23405.00 1 O'Shea Cr Random Coho Repeat 97,99,02,05 1.32 Umpqua River South Umpqua 23407.00 1 Small Cr Random Coho New 05 1.00 Umpqua River South Umpqua 23441.70 2 Days Cr Random Coho New 05 1.40 Umpqua River South Umpqua 23457.00 3 Shively Creek Random Coho Repeat 05 1.14 Umpqua River South Umpqua 23475.50 1 Stouts Cr,W Fk, Trib A Random Coho New 05 0.90 Umpqua River South Umpqua 23497.00 1 Elk Cr Random Coho New 05 1.10 Umpqua River South Umpqua 23511.00 1 Elk Cr Random Coho New 05 1.10 Umpqua River South Umpqua 23535.00 1 Stampede Cr Random Coho Pending 05 Umpqua River South Umpqua 23535.00 1 Stampede Cr Random Steelhead 06 Umpqua River South Umpqua 23550.00 1 Deep Cut Cr Random Coho New 05 1.10 Umpqua River South Umpqua 23556.00 1 Squaw Cr Random Coho New 05 0.90 Umpqua River South Umpqua 23556.00 1 Squaw Cr Random Steelhead 06 0.90 Umpqua River South Umpqua 23561.00 1 Jackson Cr Random Coho New 05 1.30 Umpqua River South Umpqua 23561.00 1 Jackson Cr Random Steelhead 06 1.30 Umpqua River South Umpqua 23564.00 2 Falon Creek Random Coho New 05 1.00 Umpqua River South Umpqua 23564.00 2 Falon Creek Random Steelhead 06 1.00 Umpqua River South Umpqua 23591.00 1 Boulder Cr Random Coho New 05 1.50 Umpqua River South Umpqua 23606.00 2 S Umpqua R Random Coho New 05 0.60 Umpqua River South Umpqua 23606.00 2 S Umpqua R Random Steelhead 06 0.60 Umpqua 2005-2006 Spawning Surveys Basin Subbasin Reach ID Seg. Survey Name Type Species Status Year(s) Surv. Miles Umpqua River Calapooya Creek 22891.50 3 Dodge Canyon Cr Random Coho New 05 0.60 Umpqua River Calapooya Creek 22891.50 3 Dodge Canyon Cr Random Steelhead 06 0.60 Umpqua River Calapooya Creek 22913.90 1 Oldham Cr Random Coho New 05 1.70 Umpqua River Calapooya Creek 22913.90 1 Oldham Cr Random Steelhead 06 1.70 Umpqua River Calapooya Creek 22932.00 1 Calapooya Cr Random Coho Repeat 01,05 1.57 Umpqua River Calapooya Creek 22938.00 1 Slide Cr Random Coho New 05 0.90 Umpqua River Calapooya Creek 22938.00 1 Slide Cr Random Steelhead 06 0.90 Umpqua River Calapooya Creek 22967.30 1 Coon Cr, Trib A, Left Fk Random Coho New 05 1.20 Umpqua River Calapooya Creek 22967.30 1 Coon Cr, Trib A, Left Fk Random Steelhead 06 1.20 Coos-Coquille 2005-2006 Spawning Surveys Basin Subbasin Reach ID Seg. Survey Name Type Species Status Year(s) Surv. Miles Tenmile Creek North Tenmile Lake 22370.00 3.1 Murphy Creek Lake Coho Annual, suspended 1.10 Tenmile Creek North Tenmile Lake 22377.00 2 Noble Cr (Std Unit) Lake Coho Annual 1.20 Tenmile Creek North Tenmile Lake 22379.30 1 Alder Creek (Std Unit) Lake Coho Annual 0.50 Tenmile Creek North Tenmile Lake 22379.70 1 Big Creek (Std Unit) Lake Coho Annual 0.50 Tenmile Creek South Tenmile Lake 22349.30 1 Adams (Rf Std Unit) Lake Coho Annual, 00no, 01no 0.70 Tenmile Creek South Tenmile Lake 22349.50 1 Adams (Mf Std Unit) Lake Coho Annual, 00no, 01no 0.80 Tenmile Creek South Tenmile Lake 22356.00 2.1 Roberts (Std Unit No 2) Lake Coho Annual, suspended 1.80 Tenmile Creek South Tenmile Lake 22357.20 1 Hatchery Creek (Main Stem) Lake Coho Annual, 00no 0.50 Tenmile Creek South Tenmile Lake 22357.40 1 Hatchery Creek (Right Fork) Lake Coho Annual, 00no 0.10 Tenmile Creek South Tenmile Lake 22357.60 1 Hatchery Creek (Left Fork) Lake Coho Annual, 00no 0.10 Tenmile Creek South Tenmile Lake 22357.80 1 Johnson (Rf Std Unit) Lake Coho Annual 0.80 Tenmile Creek South Tenmile Lake 22359.00 6 Benson Cr Random Coho New 05 1.20 Tenmile Creek South Tenmile Lake 22359.00 6 Benson Cr Random Steelhead 06 1.20 Coos River Mainstem 22088.00 2 Winchester Cr, Trib D (aka W Supplemental Coho 99,04,05 0.75 Fk Winchester Cr) Coos River Mainstem 22135.00 3 Seelander Cr Random Coho Pending 05 Coos River Mainstem 22135.00 3 Seelander Cr Random Steelhead 06 Coos River Mainstem 22310.00 1 Willanch Cr Random Coho Repeat 92,98,99,02,05 1.20 Coos River Mainstem 22310.30 1 Willanch Cr, Trib A Random Coho Repeat 05 0.71 Coos River Mainstem 22324.00 3 Palouse Cr Random Coho Repeat 01,04,05 0.22 Coos River Millicoma River 22240.00 1 Woodruff Cr Random Coho Repeat 98,99,05 1.03 Coos River Millicoma River 22240.00 1 Woodruff Cr Random Steelhead 06 1.03 Coos River Millicoma River 22242.30 1 Y Cr Random Coho Repeat 98,99,00,01,02,03,04,05 0.49 Coos River Millicoma River 22242.30 1 Y Cr Random Steelhead 03,04,05,06 0.49 Coos River Millicoma River 22246.00 1 Glenn Cr Random Coho Repeat 94,99,02,05 0.90 Coos River Millicoma River 22248.00 1 Glenn Cr Random Coho Repeat 98,04,05 0.82 Coos River Millicoma River 22265.00 1 East Fork Millicoma River Standard Fall Chinook Annual 0.50 Coos River Millicoma River 22267.00 1 Millicoma R, E Fk Random Coho Repeat 97,00,03,05 1.26 Coos River Millicoma River 22273.00 4 Millicoma R, E Fk Random Coho Repeat 93,98,99,00,01,02,03,04, 0.97 Coos River Millicoma River 22273.00 5 Millicoma R, E Fk Random Coho New 05 1.20 Coos River Millicoma River 22273.70 1 Millicoma R, E Fk Random Coho Repeat 95,01,02,03,05 1.06 Coos River Millicoma River 22276.00 2 West Fork Millicoma River Standard Fall Chinook Annual 0.50 Coos River Millicoma River 22293.00 1 Deer Cr Random Coho New 05 1.00 Coos River Millicoma River 22293.00 1 Deer Cr Random Steelhead 06 1.00 Coos River Millicoma River 22297.60 1 Elk Creek Random Coho Repeat 03,05 1.40 Coos River Millicoma River 22297.60 1 Elk Creek Random Steelhead 04,06 1.40 Coos-Coquille 2005-2006 Spawning Surveys Basin Subbasin Reach ID Seg. Survey Name Type Species Status Year(s) Surv. Miles Coos River Millicoma River 22299.00 1 Fish Cr Random Coho Repeat 93,98,99,00,01,02,03,04, 1.40 Coos River Millicoma River 22300.00 1 Millicom R, W Fk Random Coho Repeat 96,98,99,00,01,02,03,04, 0.74 Coos River Millicoma River 22300.00 1 Millicom R, W Fk Random Steelhead 03,04,05,06 0.74 Coos River Millicoma River 22302.00 1 Millicoma R, W Fk Random Coho Repeat 99,02,05 0.75 (Panther/Kelly) Coos River Millicoma River 22302.00 1 Millicoma R, W Fk Random Steelhead 06 0.75 (Panther/Kelly) Coos River Millicoma River 22306.00 2 Millicoma R, W Fk Random Coho Repeat 91,03,05 0.47 Coos River Millicoma River 22306.00 2 Millicoma R, W Fk Random Steelhead 06 0.47 Coos River South Fork 22157.00 1 Wren Smith Cr Random Coho Repeat 91,97,98,99,00,02,03,04, 1.47 Coos River South Fork 22158.00 2 Daniels Cr Random Coho Repeat 94,96,98,01,05 0.80 Coos River South Fork 22162.00 1 Besse Cr Random Coho Repeat 94,99,00,02,05 1.09 Coos River South Fork 22162.00 1 Besse Cr Random Steelhead 06 1.09 Coos River South Fork 22168.00 1 Salmon Cr Random Coho Repeat 92,05 0.82 Coos River South Fork 22177.50 1 South Fork Coos River (Farrin Standard Fall Chinook Annual 1.00 To Coal) Coos River South Fork 22185.00 1 Hatcher Cr Random Coho Repeat 98,99,00,01,02,03,04,05 0.98 Coos River South Fork 22187.00 1 Shotgun Cr Random Coho Repeat 92,95,96,05 0.84 Coos River South Fork 22187.00 2 Shotgun Cr Random Coho New 96,04,05 0.81 Coos River South Fork 22187.00 2 Shotgun Cr Random Steelhead 05,06 0.81 Coos River South Fork 22189.00 1 Susan Cr Random Coho Repeat 99,02,05 1.24 Coos River South Fork 22189.00 1 Susan Cr Random Steelhead 06 1.24 Coos River South Fork 22191.00 1 Hog Ranch Cr Random Coho Repeat 99,02,05 0.29 Coos River South Fork 22196.00 1 Tioga Cr Random Coho Repeat 92,94,99,01,02,05 1.10 Coos River South Fork 22196.60 1 Eight R Cr, Trib A Random Coho Repeat 99,02,05 0.37 Coos River South Fork 22196.60 1 Eight R Cr, Trib A Random Steelhead 06 0.37 Coos River South Fork 22196.80 1 Tioga Cr Random Coho Repeat 93,96,99,02,05 1.28 Coos River South Fork 22200.00 2 Bottom Cr Random Coho Repeat 94,01,05 0.63 Coos River South Fork 22200.40 1 Bottom Cr Random Coho Repeat 97,98,99,00,01,02,03,04, 0.44 Coos River South Fork 22200.40 1 Bottom Cr Random Steelhead 03,04,05,06 0.44 Coos River South Fork 22204.00 1 Cedar Cr (Trib A To Gods Random Coho Repeat 98,99,00,01,02,03,04,05 1.35 Thumb) Coos River South Fork 22215.00 2 Williams River A (Standard) Standard Fall Chinook Annual 1.00 Coos River South Fork 22217.60 1 Panther Cr Random Coho Repeat 93,97,99,05 1.31 Coos River South Fork 22221.00 1 Williams R Random Coho Repeat 97,98,05 1.38 Coquille River Mainstem And Bay 21610.00 1 Offield Cr Random Coho Repeat 94,05 0.98 Coquille River Mainstem And Bay 21613.00 1 Bill Cr Random Coho Repeat 97,05 1.00 Coos-Coquille 2005-2006 Spawning Surveys Basin Subbasin Reach ID Seg. Survey Name Type Species Status Year(s) Surv. Miles Coquille River Mainstem And Bay 21613.00 1 Bill Cr Random Steelhead 06 1.00 Coquille River Mainstem And Bay 21613.00 3 Bill Cr Random Coho Repeat 90,91,92,98,99,01,02,03, 1.00 Coquille River Mainstem And Bay 21613.00 5 Bill Cr Random Coho Repeat 00,02,05 0.92 Coquille River Mainstem And Bay 21613.70 2 Bill Cr Random Coho Repeat 93,98,99,01,02,04,05 1.20 Coquille River Mainstem And Bay 21620.00 2 Bear Cr Random Coho Repeat 97,05 0.82 Coquille River Mainstem And Bay 21628.00 2 Lampa Cr Random Coho Repeat 97,99,02,05 1.07 Coquille River Mainstem And Bay 21645.00 3 Fat Elk Cr Random Coho New 05 0.60 Coquille River Mainstem And Bay 21654.00 1 Cawfield Cr, Trib A Random Coho Repeat 96,99,02,05 0.83 Coquille River Mainstem And Bay 21664.00 1 Rink Cr Random Coho Repeat 94,05 0.58 Coquille River North Fork 21946.00 1 Johns Cr Random Coho Repeat 94,97,98,99,00,01,02,03, 0.87 Coquille River North Fork 21988.00 1 Wimer Cr Random Coho Repeat 97,02,05 1.60 Coquille River North Fork 22003.00 1 Cherry Cr Random Coho Repeat 92,94,05 0.79 Coquille River North Fork 22006.00 4 Middle Cr Random Coho Pending 05 Coquille River North Fork 22012.00 2 Middle Cr Random Coho Repeat 95,97,01,05 0.94 Coquille River North Fork 22014.00 2 Middle Cr Random Coho New 05 0.80 Coquille River North Fork 22014.00 4 Middle Cr Random Coho Repeat 00,03,05 0.71 Coquille River North Fork 22015.00 2 Alder Cr Random Coho Repeat 95,05 1.00 Coquille River North Fork 22015.00 2 Alder Cr Random Steelhead 06 1.00 Coquille River North Fork 22018.00 2 Middle Cr Random Coho Repeat 96,97,03,04,05 1.18 Coquille River North Fork 22024.00 2 Middle Cr Random Coho Repeat 95,00,03,05 0.84 Coquille River North Fork 22033.00 4 Woodward Cr Random Coho New 05 1.20 Coquille River North Fork 22033.00 4 Woodward Cr Random Steelhead 06 1.20 Coquille River North Fork 22036.00 4 Hudson Cr Random Coho Repeat 01,02,03,05 1.35 Coquille River North Fork 22036.00 6 Hudson Cr Random Coho Pending 05 Coquille River North Fork 22036.00 6 Hudson Cr Random Steelhead 06 Coquille River North Fork 22037.00 3 Coquille R, N Fk Random Coho Repeat 98,99,00,01,02,03,04,05 1.14 Coquille River North Fork 22037.80 1 Moon Cr, Trib A Random Coho Repeat 96,01,05 0.92 Coquille River North Fork 22037.80 1 Moon Cr, Trib A Random Steelhead 06 0.92 Coquille River North Fork 22038.00 2 Moon Cr Random Coho Repeat 94,97,05 0.88 Coquille River North Fork 22038.00 2 Moon Cr Random Steelhead 06 0.88 Coquille River North Fork 22039.00 2 Coquille R, N Fk Random Coho New 05 0.40 Coquille River North Fork 22041.00 2 North Fork (Upper-A) Standard Fall Chinook Annual 1.00 Coquille River North Fork 22041.00 2 North Fork (Upper-A) Standard Coho Annual 1.00 Coquille River North Fork 22046.00 1 L. N. Fk Cr (Trib Y) Random Coho Repeat 00,02,03,04,05 0.66 Coquille River North Fork 22046.00 1 L. N. Fk Cr (Trib Y) Random Steelhead 05,06 0.66 Coquille River North Fork 22049.00 1 Fruin Cr Random Coho New 05 1.30 Coos-Coquille 2005-2006 Spawning Surveys Basin Subbasin Reach ID Seg. Survey Name Type Species Status Year(s) Surv. Miles Coquille River North Fork 22049.00 1 Fruin Cr Random Steelhead 06 1.30 Coquille River North Fork 22051.20 1 Coquille R, N Fk Random Coho New 05 1.20 Coquille River North Fork 22051.20 1 Coquille R, N Fk Random Steelhead 06 1.20 Coquille River North Fork 22051.20 4 Coquille R, N Fk (Little N Fk To Random Coho Repeat 99,02,05 1.57 Trib I) Coquille River North Fork 22051.20 4 Coquille R, N Fk (Little N Fk To Random Steelhead 06 1.57 Trib I) Coquille River East Fork 21949.00 2 Weekly Cr Random Coho Repeat 96,97,98,05 0.97 Coquille River East Fork 21951.00 2 Elk Cr Random Coho Repeat 93,99,05 1.00 Coquille River East Fork 21951.30 1 S. Fk. Elk Cr Random Coho Repeat 98,00,05 1.06 Coquille River East Fork 21953.30 2 Yankee Run, Trib C Random Coho Repeat 99,04,05 0.97 Coquille River East Fork 21953.30 2 Yankee Run, Trib C Random Steelhead 05,06 0.97 Coquille River East Fork 21954.00 4 East Fork (Lower) Standard Fall Chinook Annual 1.00 Coquille River East Fork 21957.00 1 Steel Cr Random Coho Repeat 98,99,00,01,02,03,04,05 0.76 Coquille River East Fork 21962.00 1 East Fork (Above Dora) Standard Fall Chinook Annual 0.30 Coquille River East Fork 21965.00 1 Canyon Cr Random Coho Repeat 92,93,05 0.82 Coquille River East Fork 21965.00 1 Canyon Cr Random Steelhead 06 0.82 Coquille River Middle Fork 21734.00 1 Mcmullen Cr Random Coho Repeat 94,98,99,00,02,03,04,05 0.98 Coquille River Middle Fork 21736.00 1 King Cr Random Coho Repeat 94,05 0.73 Coquille River Middle Fork 21736.00 1 King Cr Random Steelhead 06 0.73 Coquille River Middle Fork 21741.00 1 Fall Cr Random Coho Repeat 92,05 0.69 Coquille River Middle Fork 21742.10 1 Brownson Cr Random Coho Repeat 98,99,02,05 1.24 Coquille River Middle Fork 21742.10 1 Brownson Cr Random Steelhead 06 1.24 Coquille River Middle Fork 21743.00 1 Axe Cr Random Coho Repeat 91,93,96,98,99,00,01,02, 1.10 Coquille River Middle Fork 21748.00 1 Big Cr Random Coho Repeat 93,94,04,05 1.45 Coquille River Middle Fork 21748.00 1 Big Cr Random Steelhead 06 1.45 Coquille River Middle Fork 21753.00 1 Rock Creek Random Coho Repeat 02,05 1.34 Coquille River Middle Fork 21753.00 1 Rock Creek Random Steelhead 06 1.34 Coquille River Middle Fork 21755.00 2 Rock Creek (Lower-A) Standard Fall Chinook Annual 0.50 Coquille River Middle Fork 21755.00 5 Rock Cr Random Coho Repeat 98,99,00,01,02,03,04,05 1.14 Coquille River Middle Fork 21755.00 6 Rock Cr Random Coho Repeat 91,00,02,05 1.00 Coquille River Middle Fork 21755.00 6 Rock Cr Random Steelhead 06 1.00 Coquille River Middle Fork 21758.00 1 Myrtle Cr Random Coho Repeat 96,03,04,05 1.22 Coquille River Middle Fork 21772.50 1 SANDY CR Random Coho Repeat 05 0.90 Coquille River Middle Fork 21772.90 3 Sandy Cr Random Coho Repeat 92,03,05 0.96 Coquille River Middle Fork 21775.00 2 Middle Fork Standard Fall Chinook Annual 0.50 Coos-Coquille 2005-2006 Spawning Surveys Basin Subbasin Reach ID Seg. Survey Name Type Species Status Year(s) Surv. Miles Coquille River South Fork 21699.00 2 Matheny Cr Random Coho New 05 0.80 Coquille River South Fork 21715.00 1 Catching Cr Random Coho Repeat 97,99,02,05 0.67 Coquille River South Fork 21715.00 1 Catching Cr Random Steelhead 06 0.67 Coquille River South Fork 21722.30 1 Beaverdam Br Random Coho New 05 0.20 Coquille River South Fork 21722.30 1 Beaverdam Br Random Steelhead 06 0.20 Coquille River South Fork 21724.00 2 Catching Cr, S Fk Random Coho New 05 0.90 Coquille River South Fork 21724.00 2 Catching Cr, S Fk Random Steelhead 06 0.90 Coquille River South Fork 21840.00 2 South Fork C Standard Fall Chinook Annual 1.00 Coquille River South Fork 21847.00 2 Woodward Cr Random Coho New 05 0.10 Coquille River South Fork 21849.00 1 Salmon Creek (Lower) Standard Fall Chinook Annual 0.84 Coquille River South Fork 21853.00 1 Salmon Cr Random Coho Repeat 93,97,05 0.43 Coquille River South Fork 21855.00 2 Salmon Cr Random Coho Repeat 98,05 0.91 South Coast 2005-2006 Spawning Surveys Basin Subbasin Reach ID Seg. Survey Name Type Species Status Year(s) Surv. Miles Fourmile Cr Mainstem 21560.50 1 Lower Fourmile Creek Random Coho Repeat 05 0.90 Fourmile Cr Mainstem 21560.50 1 Lower Fourmile Creek Random Steelhead 06 0.90 Fourmile Cr Mainstem 21560.76 1 Fourmile Cr Random Coho Repeat 98,99,00,01,03,04,05 1.39 Fourmile Cr Mainstem 21560.76 1 Fourmile Cr Random Steelhead 04,05,06 1.39 New River Mainstem 21566.30 4 Butte Creek (Upper) Random Coho Repeat 98,01,04,05 0.75 New River Mainstem 21566.30 4 Butte Creek (Upper) Random Steelhead 06 0.75 New River New Lake 21564.50 3 Bethel Creek Random Coho Repeat 97,98,05 1.14 Floras Creek Mainstem 21569.00 1 Willow Creek Random Coho Repeat 97,99,02,05 0.53 Floras Creek Mainstem 21569.00 2 Willow Creek Supplemental Fall Chinook 94,95,96,98,99,00,01,02, 1.50 Floras Creek Mainstem 21569.00 3 Willow Creek (Upper) Supplemental Coho 94,95,96,97,98,99,01,02, 0.48 Floras Creek Mainstem 21570.00 4 Upper Floras Creek Standard Fall Chinook Annual 0.50 Sixes River Mainstem 21534.00 1 Crystal Cr Random Coho New 05 1.00 Sixes River Mainstem 21534.00 2 Crystal Creek Supplemental Fall Chinook 94,95,96,97,98,99,00,01, 1.40 Sixes River Mainstem 21534.00 2 Crystal Creek Supplemental Coho 94,95,96,97,98,99,00,01, 1.40 Sixes River Mainstem 21534.00 3 Crystal Cr Supplemental Coho 98,99,00,01,02,04,05 1.24 Sixes River Mainstem 21540.00 1 Edson Creek (Lower) Supplemental Fall Chinook 94,95,96,97,98,99,00,01, 1.00 Sixes River Mainstem 21540.00 1 Edson Creek (Lower) Supplemental Coho 94,95,96,97,98,99,00,01, 1.00 Sixes River Mainstem 21540.00 2 Edson Creek (Upper) Supplemental Fall Chinook 94,95,96,97,98,99,00,01, 1.00 Sixes River Mainstem 21540.00 2 Edson Creek (Upper) Supplemental Coho 94,95,96,97,98,99,00,01, 1.00 Sixes River Mainstem 21542.00 1 Dry Creek(Lower) Standard Fall Chinook Annual 1.70 Sixes River Mainstem 21542.00 1 Dry Creek(Lower) Random Coho Repeat 05 1.70 Sixes River Mainstem 21542.00 2 Dry Creek(Upper) Standard Fall Chinook Annual 1.70 Sixes River Middle Fork 21552.00 1 M. Fk Sixes (Lower) Supplemental Fall Chinook 94,95,96,01,02,03,04,05 1.30 Sixes River Middle Fork 21552.00 1 M. Fk Sixes (Lower) Supplemental Coho 94,95,96,01,02,03,04,05 1.30 Sixes River Middle Fork 21552.60 1 Sixes R, M Fk Supplemental Fall Chinook 94,95,96,97,98,99,01,02, 0.90 Sixes River Middle Fork 21552.60 1 Sixes R, M Fk Supplemental Coho 94,95,96,97,98,99,01,02, 0.90 Sixes River Middle Fork 21552.60 1 Sixes R, M Fk Random Coho Repeat 05 0.90 Sixes River Middle Fork 21552.90 1 Sixes R, M Fk Random Coho New 05 0.60 Elk River Mainstem 21526.00 1 Butler Creek Random Coho Repeat 02,05 1.34 Elk River Mainstem 21531.00 1 Elk R, N Fk Random Coho New 05 0.90 Euchre Creek Mainstem 21471.00 2 Upper Euchre Creek Standard Fall Chinook Annual 1.00 Rogue River Mainstem 20195.00 1 Jim Hunt Creek Standard Fall Chinook Annual 0.80 Rogue River Mainstem 20213.00 2 Quosatana Creek Supplemental Fall Chinook 94,95,96,97,98,99,00,01, 1.50 Rogue River Mainstem 20213.00 2 Quosatana Creek Random Coho Repeat 99,02,05 1.50 Rogue River Mainstem 20215.00 1 Silver Cr Random Coho New 05 0.40 Rogue River Lobster Creek 20199.00 2 Lobster Cr Random Coho New 05 1.40 South Coast 2005-2006 Spawning Surveys Basin Subbasin Reach ID Seg. Survey Name Type Species Status Year(s) Surv. Miles Rogue River Lobster Creek 20199.00 3 Lobster Cr Random Coho New 05 0.40 Rogue River Lobster Creek 20199.00 4 Lobster Cr Random Coho Repeat 05 1.14 Rogue River Lobster Creek 20201.00 2 Lobster Creek (Upper) Standard Fall Chinook Annual 1.00 Rogue River Lobster Creek 20205.00 1 Lobster Cr Random Coho Repeat 05 1.14 Hunter Creek Mainstem 20176.00 5 Upper Hunter Creek Standard Fall Chinook Annual 1.00 Pistol River Mainstem 20161.00 2 Deep Creek Standard Fall Chinook Annual 0.90 Chetco River Mainstem 20053.00 1 Big Emily Creek Standard Fall Chinook Annual 1.00 Chetco River North Fork 20037.00 1 N. Fk Chetco River Supplemental Fall Chinook 94,95,96,97,98,99,00,01, 1.20 Winchuck River Mainstem 20011.00 1 Bear Creek Standard Fall Chinook Annual 0.80 Winchuck River Mainstem 20013.00 1 Bear Creek (Upper) Supplemental Fall Chinook 94,95,96,97,98,99,01,02, 0.50 Winchuck River Mainstem 20022.00 3 Wheeler Creek (Upper) Supplemental Fall Chinook 95,96,97,98,99,00,01,02, 0.80 Upper Rogue 2005-2006 Spawning Surveys Basin Subbasin Reach ID Seg. Survey Name Type Species Status Year(s) Surv. Miles Rogue River Mainstem 20480.00 2 Shasta Costa Creek Supplemental Fall Chinook 94,95,96,97,98,99,01,02, 1.00 Lower Willamette 2005-2006 Spawning Surveys Basin Subbasin Reach ID Seg. Survey Name Type Species Status Year(s) Surv. Miles Lower Willamette Mainstem 30863.00 2 MT SCOTT CR Random Coho 05 1.10 (Canby) Lower Willamette Mainstem 30865.50 1 TRYON CR Random Coho 05 1.00 (Canby) Lower Willamette Mainstem 30865.90 2 TRYON CR Random Coho 05 (Canby) Lower Willamette Mainstem 31200.00 2 Abernathy Cr Random Coho 05 (Canby) Lower Willamette Milton Creek 30797.50 1 Milton Creek Random Coho 02,03,04,05 0.90 (Canby) Lower Willamette Milton Creek 30800.00 3 Cox Creek Random Coho 02,03,04,05 0.99 (Canby) Lower Willamette Milton Creek 30801.00 1 Milton Creek Random Coho 02,05 0.96 (Canby) Lower Willamette Milton Creek 30802.00 2 SALMON CREEK Standard Coho Annual 0.30 (Canby) Lower Willamette Milton Creek 30807.00 3 MILTON CR Standard Coho Annual 0.30 (Canby) Lower Willamette Milton Creek 30809.00 1 Milton Creek Random Coho 03,04,04,05 1.10 (Canby) Lower Willamette Milton Creek 30809.00 3 MILTON CR Random Coho 05 0.50 (Canby) Lower Willamette Johnson Creek 30858.70 3 Johnson Creek Random Coho 04,05 1.20 (Canby) Lower Willamette Johnson Creek 30858.70 4 Johnson Creek Random Coho 02,05 1.02 (Canby) Scappoose Creek South Scappoose 30824.00 1 RAYMOND CR Standard Coho Annual 1.00 Creek Scappoose Creek South Scappoose 30824.00 1 RAYMOND CR Random Coho 05 1.00 Creek Scappoose Creek South Scappoose 30825.50 1 S Scappoose Cr Random Coho 02,05 1.10 Creek Scappoose Creek South Scappoose 30826.70 1 GOURLAY CR Random Coho 05 1.00 Creek Scappoose Creek North Scappoose 30831.00 1 SIERKS CREEK (DEEP CR.) Standard Coho Annual 0.30 Creek Clackamas River Mainstem 30896.00 2 Tickle Creek Standard Coho Annual 1.60 Clackamas River Mainstem 30896.00 2 Tickle Creek Random Coho 02,05 1.60 Clackamas River Mainstem 30900.27 2 TICKLE CR Random Coho 05 Clackamas River Mainstem 30901.00 1 Deep Creek. Random Coho 02,05 1.50 Clackamas River Mainstem 30901.00 2 Deep Creek Random Coho 04,05 1.10 Lower Willamette 2005-2006 Spawning Surveys Basin Subbasin Reach ID Seg. Survey Name Type Species Status Year(s) Surv. Miles Clackamas River Mainstem 30901.70 1 DEEP CR Standard Coho Annual 2.00 Clackamas River Mainstem 30901.70 1 DEEP CR Random Coho 04,05 2.00 Clackamas River Clear Creek 30870.00 1 Clear Creek Random Coho 05 Clackamas River Clear Creek 30870.00 4 Clear Creek Random Coho 05 Clackamas River Clear Creek 30875.10 1 Clear Creek Random Coho 05 Clackamas River Clear Creek 30878.00 1 Clear Creek Random Coho 02,04,05 0.90 Clackamas River Clear Creek 30881.00 1 LITTLE CLEAR CR Random Coho 05 0.40 Clackamas River Eagle Creek 30905.00 1 Eagle Cr Random Coho 04,05 1.30 Clackamas River Eagle Creek 30916.00 1 EAGLE CR, N FK Random Coho 05 1.40 Clackamas River Eagle Creek 30920.00 1 Eagle Cr, N Fk Random Coho 02,05 1.50 Clackamas River Eagle Creek 30921.00 3 EAGLE CR Random Coho 05 0.70 Clackamas River Eagle Creek 30923.00 4 Eagle Creek Random Coho 05 0.70 Sandy River Mainstem 33395.30 1 Arrow Cr Random Coho 05 Sandy River Mainstem 33405.00 1 BUCK CR Random Coho 05 0.40 Sandy River Mainstem 33486.00 1 Wildcat Creek Random Coho 03,04,05 0.80 Sandy River Mainstem 33536.00 2 Hackett Creek Random Coho 05 Sandy River Mainstem 33537.00 1 SANDY R Random Coho 05 3.60 Sandy River Mainstem 33538.00 2 BEAR CR Random Coho 05 0.70 Sandy River Mainstem 33564.00 2 Clear Cr Random Coho 05 Sandy River Mainstem 33570.00 1 LOST CR Random Coho 05 0.70 Sandy River Mainstem 33572.00 2 Lost Creek Random Coho 03,04,05 0.94 Sandy River Mainstem 33572.30 1 Burnt Lake Cr. Random Coho 03,04,05 0.60 Bull Run River Mainstem 33437.00 1 BULL RUN R Random Coho 05 0.90 Bull Run River Mainstem 33437.00 3 BULL RUN R Random Coho 05 Salmon River Mainstem 33489.00 2 BOULDER CR Random Coho 05 0.90 Salmon River Mainstem 33490.00 2 Salmon R Random Coho 05 Salmon River Mainstem 33491.00 1 LYMP CR Random Coho 05 0.40 Salmon River Mainstem 33497.00 1 CHEENEY CR Random Coho 05 1.30 Salmon River Mainstem 33498.30 1 TRIB A, SALMON R Random Coho 05 0.10 Salmon River Mainstem 33502.00 1 Salmon River Random Coho 03,04,05 1.30 Zigzag River Mainstem 33550.00 2 ZIGZAG R Random Coho 05 0.70 Zigzag River Mainstem 33555.00 1 CAMP CR Random Coho 05 1.10 Zigzag River Mainstem 33557.00 1 DEVIL CANYON Random Coho 05 0.40 Zigzag River Still Creek 33547.00 1 STILL CR Random Coho 05 1.00 Zigzag River Still Creek 33547.00 2 STILL CR Random Coho 05 0.90 Zigzag River Still Creek 33549.00 2 STILL CR Random Coho 05 0.70 Lower Willamette 2005-2006 Spawning Surveys Basin Subbasin Reach ID Seg. Survey Name Type Species Status Year(s) Surv. Miles Zigzag River Still Creek 33549.70 3 Still Cr Random Coho 04,05 1.10 Columbia Gorge McCord Creek 33622.00 1 McCord Creek Random Coho 05 0.44 Tributaries Columbia Gorge Moffett Creek 33625.00 1 MOFFETT CR Random Coho 05 0.70 Tributaries Columbia Gorge Eagle Creek 33637.70 1 Herman Creek Random Coho 05 1.30 Tributaries Columbia Gorge Eagle Creek 33639.00 1 Gorton Creek Random Coho 05 0.70 Tributaries Hood River 2005-2006 Spawning Surveys Basin Subbasin Reach ID Seg. Survey Name Type Species Status Year(s) Surv. Miles Columbia Gorge Bridal Veil Creek 33675.00 1 LINDSEY CR Random Coho 05 0.30 Tributaries Lower Columbia 2005-2006 Spawning Surveys Basin Subbasin Reach ID Seg. Survey Name Type Species Status Year(s) Surv. Miles Lewis and Clark River Mainstem 30032.00 1 JOHNSON CR Random Coho 05 0.40 Lewis and Clark River Mainstem 30045.00 2 LEWIS AND CLARK R Random Coho 05 0.90 Lewis and Clark River Mainstem 30049.00 1 LEWIS AND CLARK R Random Coho 05 0.80 Lewis and Clark River Mainstem 30055.00 2 LEWIS AND CLARK R Random Coho 05 1.10 Lewis and Clark River Mainstem 30055.30 1 CAMP C CREEK Random Coho 05 0.50 Lewis and Clark River Mainstem 30059.13 1 Lewis and Clark River Random Coho 03,04,05 0.80 Lewis and Clark River Mainstem 30059.16 1 TRIB A1 Random Coho 05 0.70 Lewis and Clark River Mainstem 30059.18 1 Lewis and Clark River Random Coho 03,04,05 1.38 Lewis and Clark River Mainstem 30059.26 1 TRIB C Random Coho 05 0.70 Lewis and Clark River Mainstem 30059.28 1 LEWIS AND CLARK R Random Coho 05 0.50 Youngs River Mainstem 30089.00 2 YOUNGS RIVER Standard Coho Annual 0.30 Youngs River Walluski River 30068.70 1 Wallooskee River Random Coho 03,04,05 1.30 Youngs River Klaskanine River 30086.30 1 Klaskanine River, South Fork Random Coho 02,05 0.80 Bear Creek Mainstem 30126.00 2 Little Bear Creek Random Coho 02,04,05 1.10 Columbia River Ferris Creek 30139.70 2 Ferris Creek Random Coho 05 Big Creek Mainstem 30171.00 3 LITTLE CREEK Standard Coho Annual 1.20 Big Creek Mainstem 30172.00 2 Big Creek Random Coho 02,03,04,05 1.19 Gnat Creek Mainstem 30194.00 2 SUPPLY CR Random Coho 05 0.70 Gnat Creek Mainstem 30198.70 1 Gnat Creek Random Coho 03,04,05 1.00 Hunt Creek Mainstem 30235.00 2 HUNT CREEK Random Coho 02,05 0.10 Westport Slough Mainstem 30251.00 1 EILERTSON CR Random Coho 02,05 0.41 Clatskanie River Mainstem 30276.00 1 Conyers Creek Random Coho 03,04,05 0.60 Clatskanie River Mainstem 30280.00 2 Conyers Creek Random Coho 02,03,04,05 0.90 Clatskanie River Mainstem 30285.00 1 CLATSKANIE R Random Coho 05 0.70 Clatskanie River Mainstem 30286.00 1 PERKINS CR Random Coho 05 1.00 Clatskanie River Mainstem 30289.00 3 CLATSKANIE R Random Coho 05 1.00 Clatskanie River Mainstem 30291.00 1 Clatskanie River Random Coho 04,05 0.85 Clatskanie River Mainstem 30297.00 1 Adam Creek (Page Creek) Random Coho 02,04,05 1.10 Clatskanie River Mainstem 30298.00 1 CLATSKANIE R Random Coho 05 0.90 Clatskanie River Mainstem 30298.00 2 CLATSKANIE R Random Coho 05 Clatskanie River Mainstem 30303.00 1 CARCUS CREEK Standard Coho Annual 1.30 Clatskanie River Mainstem 30306.00 1 Clatskanie River Random Coho 03,04,05 0.90 Clatskanie River Mainstem 30308.00 1 Clatskanie R Random Coho 02,05 0.84 Clatskanie River Mainstem 30308.00 3 Clatskanie River Random Coho 03,04,05 1.00 Clatskanie River Mainstem 30308.00 5 CLATSKANIE R Random Coho 05 1.10 Lower Columbia 2005-2006 Spawning Surveys Basin Subbasin Reach ID Seg. Survey Name Type Species Status Year(s) Surv. Miles Clatskanie River Mainstem 30308.50 2 WILARK UNIT (UPPER Standard Coho Annual 0.90 CLATSKANIE R) Clatskanie River Mainstem 30308.70 1 Clatskanie R, Trib 1 Random Coho 02,03,04,05 1.01 Dobbins Slough Beaver Creek 30336.00 2 Beaver Creek Random Coho 03,04,05 1.10 Goble Creek Mainstem 30652.70 1 Goble Creek, South Fork Random Coho 05 Goble Creek Mainstem 30653.50 1 Goble Creek Random Coho 02,05 1.50 Goble Creek Mainstem 30653.90 1 Goble Creek Random Coho 03,04,05 1.30 Tide Creek Mainstem 30656.60 2 Merrill Cr. Random Coho 03,04,05 0.93