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S ¸# " ¸# Mitchell E. Daniels, Jr., Governor Department of Natural Resources Division of Water Robert E. Carter, Jr., Director Aquifer Systems Map 41-B

BEDROCK AQUIFER SYSTEMS OF WABASH COUNTY,

R. 7 E. R. 8 E.

R. 6 E. R. 7 E. R. 5 E. R. 6 E. W hee ler Cre 24 22 23 ek 20 21 24 19 22 23 19 20 21 23 24 Liberty Mills C lea r C ree 3 County Road 1400 N k 1

R E

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7 32 y 31 36 t d 35

O 34 n a t 33 31 32 te u o 36 r 35 Cr o

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k North Manchester C y

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SR 114 5

T. 30 N. Disko

d S a T. 29 N. i 5 o 6 lv 1 The occurrence of bedrock aquifers depends on the original composition of the e 2 R r 3 r 4 y C e 6 5 t

rocks and subsequent changes which influence the hydraulic properties. Post- n r 3 W2 iv 1

4 u 1 e 6 5 0 2 e 0 R o depositional processes which promote jointing, fracturing, and solution activity of k 2 l C d e exposed bedrock generally increase the hydraulic conductivity (permeability) of a E o County Road 1100 N R the upper portion of bedrock aquifer systems. Because permeability in many ty n u places is greatest near the bedrock surface, bedrock units within the upper 100 o C Laketon Bog feet are commonly the most productive aquifers. 7 8 Nature Preserve 12 10 11 Laketon 8 9 8 11 12 7 Bedrock aquifer systems in the county are overlain by unconsolidated deposits of 11 12 7 9 10 varying thickness. In places, along the Wabash, Salamonie, and Mississinewa

C

Rivers, bedrock is exposed or lies within 10 feet of the surface. However, the o Ijamsvilleu County Road 1000 N

n

t E

y

bedrock surface is buried beneath more than 400 feet of unconsolidated materials E

0

R

P 0 0

in the deepest parts of a bedrock valley, which cuts across southern Wabash o

o 6

0

a n

3 y

d d

County. Most of the bedrock aquifers in the county are under confined C a

d 17 2 18

r o a

0 e 13 o

e 14 R

0

conditions. In other words, the potentiometric surface (water level) in most wells 15 k R

16 y

W 17

18 t y

17 14 13 n

completed in bedrock rises above the top of the water-bearing zone. 14 13 18 16 15 t

u

n o

u

o C The yield of a bedrock aquifer depends on its hydraulic characteristics and the C County Road 900 N nature of the overlying deposits. Shale and glacial till act as aquitards, restricting

recharge to underlying bedrock aquifers. However, fracturing and/or jointing may Servia

W

occur in aquitards, which can increase recharge to the underlying aquifers. 0 0 19 20 4 24 23

Hydraulic properties of the bedrock aquifers are highly variable. d ounty Road 850 N 21 22 a C 19 20 19 20 o 21 22 23 24

23 24 R

y

The susceptibility of bedrock aquifer systems to surface contamination is largely t

n u

dependent on the type and thickness of the overlying sediments. Because the o County Road 800 N bedrock aquifer systems have complex fracturing systems, once a contaminant C

has been introduced into a bedrock aquifer system, it will be difficult to track and

W

remediate. 0 0 30 29

3 25 26

d 28 27 a B 30 29 Two bedrock aquifer systems are identified for Wabash County. They are, from 26 25 30 29 28 o 27 26 ea 25 R r gr y a younger to older: the Silurian and Devonian Carbonates and the Maquoketa t ss n C ad 700 N Group of Ordovician age. u re County Ro o ek C y Road 700 N

Count E

0

W

0

85-01281-IR W

r 5

0

e 0

0 d

v 0 32

i 2

a 31 1

Silurian and Devonian Carbonates Aquifer System 36

R 35 o d

l d 34 a

R a 33

e 32 o

o 31 E 35 36 y

32 33 34 t

35 36 31 R

R

n

y

u

y

t

t o

n T. 29 N.

n

u C

The Silurian and Devonian Carbonates Aquifer System outcrops/subcrops u SR 16 o

o T. 28 N. C throughout nearly all of Wabash County. This aquifer system consists primarily C Stockdale SR 16 of Silurian age carbonates and middle Devonian age carbonates of the T. 29 N. T. 28 N. Muscatatuck Group, which subcrop only along the northern county line. Total S Roann ilv 5 thickness of this aquifer system ranges from 0 to about 500 feet. 1 6 e 2 r 4 3 C 6 5 r 2 1 e 6 5 4 3 ek Wells completed in the Silurian and Devonian Carbonates Aquifer System are 2 1 generally capable of meeting the needs of domestic and some high-capacity users

C

in this county. Reported domestic wells utilizing this system in Wabash County Urbana o

u

C

n

have depths ranging from 32 to 514 feet, but are typically 100 to 200 feet deep. C

t o

y

o

u

u

R The amount of rock penetrated in this system commonly ranges from 30 to 90 n

n

t

o W

y

t 8

y 7 a

0 12 R feet. Solution features (caves) are described on a few well records suggesting d 11 R

0 P

a o 10 6

6 w

o 8 9

7 a minor karst development. Typical yields for domestic wells range from 10 to 35 P 5 a

d a12 d w 0

11 d a 10 9 C 3 8 E o 7 r gallons per minute (gpm). Static water levels are generally 20 to 55 feet below 1 12 ee 0 0 R k

0 11

0

y

E land surface. There are 5 registered significant ground-water withdrawal facilities t 400 N

E County Road n

(16 wells). Reported yields from the individual wells are 35 to 1500 gpm. u o

C County Road 400 N

In most of Wabash County the Silurian and Devonian Carbonates Aquifer System W 17 0 13 18

has a low susceptibility to surface contamination because thick clay deposits 0 14 3 17 16 15 overlie the system. However, in areas where overlying clays are thin or absent, d 13 18 a 14

o 15 18 17 16 the system is at moderate to high risk to contamination. R

14 13 k y

t e e

n r u

o County Road 300 N C

C o

r E County Road 300 N g

a 0 0

Ordovician -- Maquoketa Group Aquifer System W

L 6

W

0

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5 20 W

0 19

24 a

1 0

23 5

3 o

4 22

d 7

21

1

20 R

a

6

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o 24 a

23 y

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Bac 22 R h o elor Creek R

In Wabash County, the Maquoketa Group subcrops only in the buried pre-glacial a

21 n

19 20 S

R o y

24 u

23 t

o

R

y

n

valley where the overlying Silurian and Devonian bedrock has been removed by

t

C

u

y

n

t

o u

erosion. The Maquoketa Group consists mostly of shales with interbedded n County Road 200 N

o C

u Speicherville C limestone units. In general, this system ranges from 525 to 600 feet thick in the o C 24 county. However, no known wells utilize this aquifer system in Wabash County 25 30 27 26 29 because the Maquoketa Group lies about 275 to 425 feet below the ground surface No. 35 ME-CHA-NE-QUA 28 and adequate water supplies are typically found in the overlying unconsolidated 30 29 26 25 County R 27 k deposits. This aquifer system has a low susceptibility to surface contamination 30 oad 150 N 29 28 ee 85-00020-PS 26 25 r 50 N because thick clay deposits cover the subcrop area. C Road 1 rt County No. 4 J.B. RICHARDVILLE k a e ye re n SR 524 LA GROS ad 50 N C E Lagro nty Ro ty Road 100 N Cou Coun er 34 tn en 32 K 33 31 32 31 35 36 34 36 31 32 33 85-01966-IR 35 36 35 T. 28 N. S 4 R T. 27 N. 1 5 4 S al am T. 28 N. 5 o

5 n County Road 50 S 5 W

W 6

1 i

T. 27 N. No. 14 J.B. RICHARDVILLE 2 e 1 0 1 0 6 R

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u

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C C c County Road 100 S n 10 12 No. 15 KA-TAH-MONG-QUAH a 8 r No. 6 MONG-GO-SAH 7 11 12 B 10 9

24 11 9 8 n 7 8 i 12 11 l WIFE AND CHILDREN OF CHARLEY r

a No. 17 TOW-WAH-KEO-SHEE 7

C Wabash County Road 200 S 16 14 17 15 County Road 250 S 13 18 16 15 14 17 18 17 18 Bu rr 13 13 Cr 14 eek No. 55 J.B. RICHARDVILLE No. 18 J.B. RICHARDVILLE Salamonie Lake

Richvalley No. 23 FRANCOIS GODFROY No. 19 F. GODFROY

E

0

0 2 20 d County Road 350 S 19 24 a 23 24

No. 13 ME-CHA-NE-QUAH o 22 20 21 19 R

23 y

24 t

21 n 23 u 20 22 o No. 11 POQUA GODFROY C County Road 400 S

Location Map 19 30 W

No. 21 AL-LO-TAH

3 0

1 T

5 29

W r 1 e 30

25 R

0 a 26

d t 27 5 28 S y a 29

5 o No. 12 CATHERINE GODFROY 26 25 C

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28 R e

a 29 e y

o 30 k

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R n 25 ounty Road 500 S

u Lincolnville C

y

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26 u 85-02509-PS

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County Road 500 S

0

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7 3

R M idg

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i y a 32 l Cr a 31

l ee o k o 36

C 34 35 R

33 R 32

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e 36 No. 20 MAIS-SHIL-GOUN-MU-ZAH t

e 35 t 34 n

k 33 n 32 u

31 u 36 o

35 o T. 27 N. C C SR 124 T. 26 N.

T. 27 N. SR 124

T. 26 N. W 5

W

1 6 0

0 2

5 3

5 4

6 5 7

6

1

d 2

d 3 a 4 a 5 o 6

o 2 1

R

R

y Road 700 S

y ounty

t C

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C oad 700 S County R 0 Creek

Treaty 0 Treaty

2

W d

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5

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8

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11 t a

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0 800 S

R County Road

n

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3

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7

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13 4 850 S 18 u No. 25 OZ-SAQ Road y County

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18 16 C t

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14 o C y County Road 900 S ou t n C t R y Ro n ad 65 u S

0 W o C

No. 26 20 24 19 22 23 20 21 County Road 950 S 24 19 22 23 S Mississinewa Lake 20 21 R 23 1 5 County Road 1000 S 24 19

29 29 25 25 30 27 26 30 28 La Fontaine 27 26 30 29 28 26 25 85-00570-PS No. 4 SR 218 Mount Somerset 32

County Road 1100 S Vernon ek W e

No. 4 r

0 C 33 0 ah 1 n 32 No. 2 36 31 ci d No. 3 34 35 o a 33 et

34 35 o No. 4 32 M R 31 32 No. 5 FLOAT CLAIM 36

35 36 y t

n T. 26 N. u o T. 25 N. C 31

T. 26 N. R. 7 E. R. 8 E. T. 25 N. R. 6 E. R. 7 E. R. 5 E. R. 6 E.

EXPLANATION Registered Significant Ground- Water Withdrawal Facility Stream County Road

State Road & US Highway

Municipal Boundary

1 0.5 0 1 Mile State Managed Property

Lake & River

1 0.5 0 1 Kilometer

Map Use and Disclaimer Statement This map was created from several existing shapefiles. Township and Range Lines of Indiana (line shapefile, 20020621), Land Survey Lines of Indiana (polygon shapefile, 20020621) and We request that the following agency be acknowledged in products derived Bedrock Aquifer Systems of Wabash County, Indiana County Boundaries of Indiana (polygon shapefile, 20020621), were all from the Indiana from this map: Indiana Department of Natural Resources, Division of Water. Geological Survey and based on a 1:24,000 scale, except the Bedrock Geology of Indiana by (polygon shapefile, 20020318), which was at a 1:500,000 scale. Draft road shapefiles, System1 Map generated by Shirley A. Fitzwater and Andrew G. Dunkman This map was compiled by staff of the Indiana Department of Natural IDNR, Division of Water, Resource Assessment Section and System2 (line shapefiles, 2003), were from the Indiana Department of Transportation and Glenn E. Grove Resources, Division of Water using data believed to be reasonably accurate. based on a 1:24,000 scale. Populated Areas in Indiana 2000 (polygon shapefile, 20021000) was However, a degree of error is inherent in all maps. This product is distributed Division of Water, Resource Assessment Section from the U.S. Census Bureau and based on a 1:100,000 scale. Streams27 (line shapefile, “as is” without warranties of any kind, either expressed or implied. This map 20000420 was from the Center for Advanced Applications in GIS at Purdue University. is intended for use only at the published scale. Managed Areas 96 (polygon shapefile, various dates) was from IDNR. November 2007 ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿

￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿

￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿

￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿

￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿

￿￿ ￿￿

￿￿ ￿￿￿￿ ￿￿ ￿￿￿￿

￿￿￿￿ ￿￿￿￿ ￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿ ￿￿

￿￿ ￿￿

￿￿￿￿ ￿￿￿￿ ￿￿ ￿￿

￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿

￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿ Wabash County, Indiana is located in the north-central portion of the state with all of the areal «¬13 ￿￿ ￿￿ ￿￿ extent of the county situated within the Upper Basin.

￿￿

￿￿ ￿￿￿￿

￿￿

￿￿￿￿ ￿￿

￿￿ ￿￿￿￿ ￿￿￿￿

￿￿ ￿￿￿￿

￿￿

￿￿ ￿￿

￿￿￿￿ ￿￿ ￿￿￿￿

￿￿ The potentiometric surface mapped (PSM) contour elevations represent lines of equal elevation

￿￿ ￿￿

￿￿ ￿￿￿￿ ￿￿￿￿

￿￿ ￿￿

￿￿￿￿ ￿￿

￿￿ ￿￿ ￿￿￿￿ ￿￿

￿￿￿￿ ￿￿

￿￿ ￿￿￿￿ relative to the measured groundwater levels in wells. In general, wells completed in a confined ￿￿ ￿￿￿￿ ￿￿

￿￿ ￿￿

Lotz ￿￿

￿￿

￿￿

￿￿

￿￿ ￿￿

￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ aquifer system are bound by impermeable layers and will have static water levels under ￿￿

Lake ￿￿ ￿￿

￿￿ hydrostatic pressure causing the water level to rise above the elevation of the aquifer resource.

￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿

￿￿ In contrast, an unconfined aquifer system is not bound by impermeable layers; therefore, the

￿￿

￿￿

Brown ￿￿ water level will not be under hydrostatic pressure and will not rise above the aquifer resource.

￿￿ ￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿ Lake ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ Static water level measurements in individual wells used to construct the potentiometric surface ￿￿￿￿ ￿￿￿￿ map are indicative of the water level at the time of well completion. Therefore, current site ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ North Manchester specific conditions may differ due to local or seasonal variations in measured static water levels. Twin ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ Lakes ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ «¬114 Coordinate locations of water well records were physically obtained in the field, determined through address geocoding, or reported on water well records. Elevation data were either ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ Disko «¬114 obtained from topographic maps or a digital elevation model (DEM). Elevation and location ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿ ￿￿ ￿￿ ￿￿ quality control/quality assurance procedures were utilized to refine or remove data where errors ￿￿

￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿

￿￿ ￿￿ were readily apparent. ￿￿ ￿￿

￿￿ ￿￿ ￿￿ ￿￿

￿￿

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￿￿ Long In Wabash County depth to bedrock varies from exposure along parts of the Wabash, ￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ Lake Mississinewa, and Salamonie rivers; to as much as 400 feet where a bedrock valley cuts across

￿￿ the southern part of the county (Grove, 2007). Wells completed in bedrock are generally

￿￿

￿￿

Mud ￿￿ Laketon Bog ￿￿ ￿￿ ￿￿ ￿￿ completed in carbonate deposits of the Silurian and Devonian Carbonates Aquifer System. ￿￿ ￿￿ Mc Calley ￿￿ ￿￿ Lake Nature Preserve ￿￿￿￿ ￿￿ ￿￿ ￿￿ ￿￿￿￿ ￿￿

￿￿￿￿ ￿￿ There are approximately 671 located wells that are completed in bedrock and utilized towards ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ Lake ￿￿ ￿￿￿￿ ￿￿

￿￿ ￿￿￿￿￿￿￿￿ ￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿ ￿￿

￿￿ ￿￿ the mapping of the bedrock potentiometric surface. However, portions of the county are lacking ￿￿ ￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿

￿￿￿￿ ￿￿ ￿￿ 15 ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ in data and/or covered by more prolific unconsolidated deposits that limit the necessity to

￿￿ «¬ Laketon ￿￿

￿￿ complete wells in bedrock. Therefore, potentiometric surface elevations contours have not been Lukens ￿￿ Round

￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿

￿￿ extended through these areas.

Lake ￿￿ Lake

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￿￿ ￿￿￿￿ Potentiometric surface elevations range from a high of 820 feet mean sea level (msl) in the

13 ￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿

￿￿ ¬ ￿￿￿￿ ￿￿ ￿￿￿￿ « ￿￿ ￿￿￿￿ southeast region of the county, to a low of 670 feet msl in the central part of the county along the ￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿ ￿￿ ￿￿￿￿ Wabash River. Generalized groundwater flow direction for Wabash County is towards major

￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿

￿￿￿￿ ￿￿ drainage relevant to the basin. Therefore, in the Upper Wabash River Basin, groundwater flow is ￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ towards the Wabash River and its major . These include the Eel River to the north, the Ijamsville

￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ Salamonie River in the east-central part of the county, and the to the south. ￿￿

￿￿ Servia

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￿￿ ￿￿ l River ￿￿ ￿￿￿￿ Grove, 2007, Bedrock Aquifer Systems of Wabash County, Indiana: Indiana Department of

e ￿￿ ￿￿￿￿ ￿￿ ￿￿

E ￿￿￿￿ ￿￿ ￿￿

￿￿ ￿￿￿￿ ￿￿￿￿￿￿ ￿￿ ￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿ ￿￿

￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿ ￿￿ Natural Resources, Division of Water, Aquifer Systems Map 41-B.

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￿￿￿￿ ￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿

￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿￿￿￿￿ ￿￿ ch ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ Dit y d

￿￿ o ￿￿￿￿ s C ￿￿ gras ree ￿￿ b

r ￿￿ a ￿￿￿￿ ea k ￿￿￿￿ B ￿￿ e ￿￿￿￿ ￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿

P ￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿ ￿￿￿￿

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￿￿ ￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿ Stockdale ￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ 16 ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ «¬ ￿￿ Roann ￿￿ ￿￿￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ Location Map Urbana

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￿￿￿￿ ￿￿ ￿￿ ￿￿￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿￿￿ ￿￿

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￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿ ￿￿ ￿￿ ￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿

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￿￿￿￿ ￿￿￿￿ ￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿ ￿￿￿￿

￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿

￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ Speicherville ￿￿￿￿ ￿￿￿￿ ￿￿￿￿

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￿￿￿￿ ￿￿ Kent ek ￿￿ ￿￿￿￿

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e r ￿￿ r C ￿￿ ￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿

￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿

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￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿ Lagro ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿

￿￿ 524 ￿￿ ￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿ «¬ Wab er ￿￿ ￿￿￿￿ ash Riv ￿￿￿￿

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￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿

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￿￿ ￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿ ￿￿ ￿￿ ￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿￿￿ ￿￿ «¬115

￿￿ ￿￿ ￿￿ ￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿ ￿￿ Salamonie ￿￿ ￿￿ ￿￿￿￿ State Forest ￿￿ ￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿ ￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿ ¤£24 ￿￿

￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿ ￿￿￿￿ Wabash ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ r ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ve ￿￿￿￿￿￿ ￿￿ ￿￿￿￿ Ri Richvalley sh ba ￿￿￿￿￿￿ Hillshade Map of Wabash County, Indiana Wa ￿￿￿￿￿￿ Salamonie Lake

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￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿

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￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿

￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿ ￿￿

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￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ «¬13 ￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ Lincolnville ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿

￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿ Asherwood ￿￿￿￿ ￿￿￿￿ ￿￿ ￿￿￿￿

￿￿￿￿ ￿￿

Nature Preserve ￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿

124 ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ «¬ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ Treaty

￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿ ￿￿ 15 ￿￿ «¬ ￿￿￿￿

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￿￿ ￿￿ ￿￿ ￿￿￿￿

￿￿￿￿ ￿￿

￿￿￿￿ ￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿ ￿￿

￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿ ￿￿ ￿￿￿￿ ￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿￿￿ ￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿

￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿

￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ Mississinewa ￿￿￿￿ ￿￿￿￿ Lake ￿￿￿￿ ￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿

￿￿ ￿￿￿￿ State Recreational ￿￿ ￿￿￿￿ ￿￿ ￿￿ ￿￿ Area ￿￿￿￿ La Fontaine ￿￿ ￿￿￿￿ ￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿ ￿￿ ￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ EXPLANATION ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿ ￿￿￿￿ Mississinewa 218 ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿ «¬ 700 ￿￿￿￿ Lake ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿

Mount Vernon ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿

￿￿ ￿￿

￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿

￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿ ￿￿ ￿￿￿￿ ￿￿ ￿￿ ￿￿￿￿ ￿￿ ￿￿

￿￿ ￿￿ ￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿ ￿￿￿￿

￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿

￿￿ ￿￿

￿￿ ￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿ 13 ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿

￿￿ Somerset «¬ ￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ¤£24 ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿

￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿ ￿￿￿￿￿￿ ￿￿ ￿￿￿￿￿￿￿￿￿￿

￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿

￿￿ ￿￿￿￿￿￿ ￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ® ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿

Map Use and Disclaimer Statement ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ Potentiometric Surface Map of the Bedrock Aquifers ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ of Wabash County, Indiana ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ Mitchell E. Daniels, Jr., Governor Department of Natural Resources Division of Water Robert E. Carter, Jr., Director Aquifer Systems Map 41-A

UNCONSOLIDATED AQUIFER SYSTEMS OF WABASH COUNTY, INDIANA

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R. 6 E. R. 7 E. R. 5 E. R. 6 E. 85-00584-IR W hee ler Seven unconsolidated aquifer systems have been mapped in Wabash County: the Cre 24 22 23 ek Till Veneer; the Bluffton Till; the Bluffton Till Subs ystem; the Bluffton Complex; 20 21 24 19 the Natural Lakes and Moraines; the Wabash River and Tributaries Outwash 22 23 19 20 21 System; and the Wabash River and Tributaries Outwash Subsystem. Boundaries 23 24 Liberty Mills C 85-03190-IR lea of these aquifer systems are commonly gradational and individual aquifers may r C ree 3 extend across aquifer system boundaries. County Road 1400 N k 1 R

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In Wabash County, the thickness of unconsolidated sediments is quite variable. 0 25

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Bedrock is at or near the surface in places along the Wabash River and some a 29

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27 R 1 o tributaries. However, the thickness of unconsolidated sediments exceeds 400 feet o 28

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in a buried bedrock valley, which enters the county near La Fontaine and trends y o

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o C u northwest and exits into Miami County near the Wabash River. Additionally, u E r

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unconsolidated deposits are over 300 feet thick in the northwest corner of Wabash County Road 1300 N

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County. Elsewhere in the county, the unconsolidated deposits are commonly 50 4

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to 125 feet thick. In Wabash County, abo ut half of the reported wells are finished 36 o

0 34 35 R 0 33 in the unconsolidated deposits.

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Regional estimates of aquifer susceptibility to contamination from the surface can k North Manchester C y

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differ considerably from local reality. Variations within geologic environments n 85-01216-PS

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can cause variation in susceptibility to surface contamination. In addition, man - 0

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made structures such as poorly constructed water wells, unplugged or improperly T. 30 N. Disko

d S a T. 29 N. i 5 o 6 abandoned wells, and open excavations can provide contaminant pathways that lv 1 e 85-00734-IR 2 R r 3 4 y

bypass the naturally protective clays. r t C e 6 5 r 3 W2 v 1 n

4 u 1 e 6 5 0 i 2 e 0 o k 2 R l C d e a E o County Road 1100 N R Till Veneer Aquifer System ty n u o C Laketon Bog 85-01503-IR 7 8 Nature Preserve 12 In Wabash County, the Till Veneer Aquifer System encompasses areas where the 10 11 Laketon 8 9 unconsolidated material is predominantly thin glacial till and/or alluvium 8 11 12 7 11 12 7 9 10 overlying an eroded bedrock surface. This system is mapped primarily in the 85-02923-PS

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southern half of the county, along portions of the Wabash River, the Mississinewa o Ijamsvilleu County Road 1000 N

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River, and the Salamonie River. Total thickness of the Till Veneer Aquifer 85-00686-IN y

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System generally ranges from about 20 to 50 feet. o

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e 14 R This system has the most limited ground-water resources of the unconsolidated 0

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aquifer systems in Wabash County. Potential aquifers within the Till Veneer 17 14 13 n

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Aquifer System are primarily thin isolated sand and/or gravel layers. Therefore, u o 85-04238-IR C very few of the reported wells penetrating this aquifer system are completed in the C County Road 900 N unconsolidated materials, which are bypassed in favor of the more productive

underlying bedrock. Servia

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0 0 19 20 4 24 This system is not very susceptible to contamination from surface sources because 23

d ounty Road 850 N 21 22 a C 19 20 the near-surface materials generally have low permeability. However, there are 19 20 o 21 22 23 24

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areas where unconsolidated deposits are extremely thin. These areas are very t n

susceptible to contamination. u o County Road 800 N

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Bluffton Till Aquifer System 0 30 29

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d 28 27 a B 30 29 26 25 30 29 28 o 27 26 ea 25 R r gr y a t ss The Bluffton Till Aquifer System is mapped mostly in the northern half of the n C ad 700 N u re County Ro county and primarily consists of thick clay with intratill sand and gravel layers. o ek

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In Wabash County, this system ranges in thickness from about 50 feet to more

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than 275 feet, but is typically 80 to 120 feet thick. Saturated aquifer materials

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include sands and/or gravels that commonly range from 5 to 15 feet thick and are 1

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generally overlain by 40 to 80 feet of till. e 32 o

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In Wabash County, most of the wells in this system are completed in the n

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underlying bedrock; however, the Bluffton Till Aquifer System is generally C C capable of meeting the needs of most domestic and some high-capacity users. T. 29 N. SR 16 T. 28 N. 85-02288-PS Wells producing from the Bluffton Till Aquifer System are generally 65 to 140 S Roann ilv 5 feet deep. Domestic well capacities are typically 10 to 60 gallons per minute 1 6 e 2 r 4 3 C (gpm) and static water levels are commonly 20 to 60 feet below the surface. 6 5 r 2 1 e 6 5 4 3 ek 2 1 The Bluffton Till Aquifer System has a low susceptibility to surface

contamination because intratill sand and gravel units are generally separated from C

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Bluffton Till Aquifer Subsystem d a12 d w 0

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Areas where unconsolidated materials are generally greater than 50 feet in o

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thickness, yet have limited aquifer potential, are mapped as the Bluffton Till County Road W Aquifer Subsystem in Wabash County. This subsystem is mapped in about 17 17 0 13 18

percent of the county. This subsystem ranges from about 50 to 220 feet thick, but 0 14 3 17 16 15 d 13 18 is typically less than 100 feet thick. Potential aquifer materials include thin, a 14

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intratill sand and gravel deposits. Where present, aquifer materials are capped by 14 13 k y

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till that is generally 40 to 120 feet thick. n r u

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More than 80 percent of wells started in the Bluffton Till Aquifer Subsystem in a 0

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Wabash County are completed in the underlying bedrock aquifer system.

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in the county. The few wells producing from the Bluffton Till Aquifer Subsystem 23 y

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are completed at depths of 50 to 218 feet. 23 t

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This subsystem is generally not very susceptible to surface contamination because u Speicherville

C o intratill sand and gravel lenses are overlain by thick till deposits. Wells producing C 24 25 30 from shallow aquifers are moderately susceptible to contamination. 27 26 29 No. 35 ME-CHA-NE-QUA 28 30 29 26 25 County R 27 k 30 oad 150 N 29 28 ee 26 25 r 50 N Bluffton Complex Aquifer System C Road 1 rt County No. 4 J.B. RICHARDVILLE k ea ee y N r n SR 524 LA GROS oad 50 C E Lagro unty R County Road 100 N r Co The Bluffton Complex Aquifer System is mapped over a large portion of Wabash e 34 tn County. This aquifer system is characterized by deposits that are quite variable in en 32 K 33 materials and thickness. A thick till commonly overlies sand and gravel aquifer 31 32 31 35 36 34 36 deposits. This system generally has multiple layers of intratill sands and gravels 31 32 33 35 36 35 T. 28 N. S 4 of various thickness and lateral extent. The main aquifer deposits are typically R T. 27 N. 1 deeper, thicker, and more continuous than the shallower sands and gravels in this 5 4 S system. In Wabash County, this system is up to 250 feet thick. Saturated aquifer al am materials in the Bluffton Complex Aquifer System are generally 10 to 25 feet T. 28 N. 5 o

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thick and are overlain by a till cap which is commonly 30 to 75 feet thick. 1 0 6 R

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This system is capable of meeting the needs of domestic and most high-capacity o

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users in Wabash County. Wells in this system are typically completed at depths y 4 t

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of 75 to 125 feet. Domestic well yields are commonly 10 to 60 gpm and static u

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C C water levels are generally 20 to 50 feet below the surface. There are 10 registered c County Road 100 S n 10 12 No. 15 KA-TAH-MONG-QUAH significant ground-water withdrawal facilities (20 wells) utilizing this system and a 8 r No. 6 MONG-GO-SAH 7 11 12 B 10 individual wells produce 130 to 1500 gpm. 9

24 11 9 8 n 7 8 Part of the Bluffton Complex Aquifer System overlies a deep i 12 11 l WIFE AND CHILDREN OF CHARLEY buried bedrock valley in southern Wabash County. The total r a No. 17 TOW-WAH-KEO-SHEE 7 unconsolidated thickness exceeds 400 feet in many places. Only a C Wabash few wells that utilize the deeper aquifers within the buried bedrock County Road 200 S 85-01292-IN 16 valley have been reported. These wells indicate that the deep 14 17 15 County Road 250 S 13 18 sand and gravel deposits are 10 to 60 feet thick in places. Reported 16 15 14 17 18 17 domestic well yields are greater than 50 gpm and high-capacity 18 Bu rr wells yield in excess of 300 gpm. 13 13 Cr 14 eek No. 55 J.B. RICHARDVILLE No. 18 J.B. RICHARDVILLE Salamonie Lake

The Bluffton Complex Aquifer System is not very susceptible to contamination Richvalley No. 23 FRANCOIS GODFROY No. 19 F. GODFROY E

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because thick clays overlie the aquifer materials. 0

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No. 13 ME-CHA-NE-QUAH o 22 20 21 19 R

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Natural Lakes and Moraines Aquifer System 21 n 23 u 20 22 o No. 11 POQUA GODFROY C County Road 400 S

The Natural Lakes and Moraines Aquifer System in Wabash County is mapped 19 30 W

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north of the Eel River and is a complex aquifer system typically with multiple 0

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intratill sand and gravel seams. Unconsolidated deposits range in thickness from 0 a 26

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5 o about 100 feet to over 250 feet. Thick surficial clays predominate and are No. 12 CATHERINE GODFROY 26 25 C

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generally 50 to 110 feet thick. A few localized surficial sand and gravel deposits o 30 k

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are reported and range from 20 to 50 feet thick; however, the static water levels y 85-00562-PS

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are typically deep and these deposits are seldom used. 26 u

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This system is capable of meeting the needs of domestic and some high-capacity e d wa d

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users in Wabash County. Wells completed in this aquifer system range in depth C 34 35 R

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from 30 to 241 feet deep. However, the wells are typically 60 to 130 feet deep. e 35 t 34 n

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Aquifer thickness is generally between 15 and 30 feet thick. In addition, several 36 o

35 85-02509-PS o T. 27 N. C areas have two or more aquifers ranging in thickness from 5 to 15 feet. Domestic C SR 124 T. 26 N. well yields are commonly 10 to 75 gpm and static water levels are typically 15 to 50 feet below the surface. There are 2 registered significant ground-water T. 27 N. SR 124 withdrawal facilities (4 wells) utilizing this system with individual wells

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1 6 0 producing up to 70 gpm. 0 2

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The Natural Lakes and Moraines Aquifer System is generally not very susceptible o 2 1

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to surface contamination because thick clay deposits overlie intratill sand and t

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gravel seams. Wells producing from shallow aquifers are moderately to highly o

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C oad 700 S susceptible to contamination. County R 0 Creek

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Wabash River and Tributaries Outwash Aquifer System 11 o 8 9 u

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The Wabash River and Tributaries Outwash Aquifer System is mapped along the

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Eel River and along the Wabash River in the western portion of the County. o

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Large amounts of outwash sand and gravel from the receding glaciers were 13 y

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13 4 deposited in the stream valley. This system exceeds 150 feet in thickness in a few 850 S 18 u No. 25 OZ-SAQ Road y County

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places with up to 90 feet of continuous sand and gravel in some places. However, 17 u

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the outwash is typically 25 to 75 feet thick with the thickness of saturated sands 14 o C y County Road 900 S ou t n C t R and gravels generally ranging from 15 to 50 feet. In some areas 10 to 45 feet of y Ro n ad 65 u S 0 W o

sandy clay or silt occurs at the surface or below the surficial sand and gravels. C No. 26 20 These sand and gravel deposits have adequate potential for domestic and most 24 19 22 23 20 21 high-capacity users. Well depths are commonly 40 to 100 feet. Domestic well County Road 950 S 24 19 22 23 S yields are commonly 10 to 60 gpm and static water levels are generally 10 to 25 Mississinewa Lake 20 21 R 23 1 feet below the surface. Five registered significant ground-water withdrawal 5 County Road 1000 S 24 facilities (10 wells) currently use the Wabash River and Tributaries Outwash 19 Aquifer System in Wabash County. Reported yields for high-capacity wells in this aquifer system are 100 to 1100 gpm. 29 29 25 25 30 27 26 30 28 La Fontaine In places, this system overlies a deep buried bedrock valley. The 27 26 30 29 28 85-02220-PS total unconsolidated thickness exceeds 300 feet in many places. 26 25 The few wells that use the deeper aquifers of the buried valley Mount No. 4 SR 218 Somerset Vernon have sand and gravel thicknesses that typically range from 20 to 32

over 45 feet. Reported domestic well yields are greater than 50 County Road 1100 S ek W e

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0 C gpm and there are no high-capacity wells in the buried valley but 33 0 ah 1 n 32 No. 2 36 31 ci yields would be expected to be in excess of 500 gpm. d No. 3 34 35 o a 33 et 34 35 o No. 4 32 M

R 31 32 No. 5 FLOAT CLAIM 36 35 36 y This aquifer system is highly susceptible to contamination from surface sources in t 85-02938-PS

n T. 26 N. u areas that lack overlying clay layers. The system is only moderately susceptible o T. 25 N. where it is overlain by thick clay or silt deposits. C 31 T. 26 N. R. 7 E. R. 8 E. T. 25 N. R. 6 E. R. 7 E. R. 5 E. R. 6 E. Wabash River and Tributaries Outwash Aquifer Subsystem

This system is primarily mapped along part of the Eel River in northern Wabash County and along portions of the Wabash River along the Miami County line and Location Map the city of Wabash. Saturated sand and gravel layers are generally 7 to 20 feet thick and are commonly overlain by silt, sandy clay, or clay ranging from 10 to 30 feet thick.

The Wabash River and Tributaries Outwash Aquifer Subsystem has the potential to meet the needs of domestic and some high-capacity users. Few wells utilize this system in Wabash County. There is an only one registered high-capacity facility (5 wells) with reported yields up to 350 gpm. EXPLANATION

Areas within this aquifer system that have overlying clay or silt deposits are Registered Significant Ground- moderately susceptible to surface contamination; whereas, areas that lack Water Withdrawal Facility overlying clay or silt deposits are highly susceptible to contamination. Stream County Road

State Road & US Highway

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Map Use and Disclaimer Statement This map was created from several existing shapefiles. Township and Range Lines of Indiana (line shapefile, 20020621), Land Survey Lines of Indiana (polygon shapefile, 20020621), Unconsolidated Aquifer Systems of Wabash County, Indiana We request that the following agency be acknowledged in products derived and County Boundaries of Indiana (polygon shapefile, 20020621), were all from the Indiana from this map: Indiana Department of Natural Resources, Division of Water. Geological Survey and based on a 1:24,000 scale. Draft road shapefiles, System1 and System2 by Map generated by Shirley A. Fitzwater and Andrew G. Dunkman (line shapefiles, 2003), were from the Indiana Department of Transportation and based on a 1:24,000 IDNR, Division of Water, Resource Assessment Section This map was compiled by staff of the Indiana Department of Natural scale. Populated Areas in Indiana 2000 (polygon shapefile, 20021000) was from the U.S. Census Glenn E. Grove Resources, Division of Water using data believed to be reasonably accurate. Bureau and based on a 1:100,000 scale. Streams27 (line shapefile, 20000420) was from the Center Division of Water, Resource Assessment Section However, a degree of error is inherent in all maps. This product is distributed for Advanced Applications in GIS at Purdue University. Managed Areas 96 (polygon shapefile, various “as is” without warranties of any kind, either expressed or implied. This map dates) was from IDNR. Unconsolidated aquifer systems coverage (Grove, 2007) was based on a is intended for use only at the published scale. 1:24,000 scale. November 2007 ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿

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￿￿ ￿￿￿￿ ￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿ ￿￿ ￿￿ ￿￿￿￿ Lotz ￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ Wabash County, Indiana is located in the north-central portion of the state with all of the areal

Lake ￿￿￿￿￿￿ ￿￿ extent of the county situated within the Upper Wabash River Basin. ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿ ￿￿

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Lake ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿￿￿ ￿￿ ￿￿ ￿￿￿￿ The mapped potentiometric surface (PSM) contour elevations represent lines of equal elevation

￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ relative to the measured groundwater levels in wells. In general, wells completed in a confined ￿￿￿￿￿￿ Twin ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ aquifer system are bound by impermeable layers and will have static water levels under ￿￿ Lakes ￿￿￿￿ ￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿ North hydrostatic pressure causing the water level to rise above the elevation of the aquifer resource. ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ In contrast, an unconfined aquifer system is not bound by impermeable layers; therefore, the Manchester 114 «¬ water level will not be under hydrostatic pressure and will not rise above the aquifer resource. ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ Disko «¬114 Static water level measurements in individual wells used to construct the potentiometric surface ￿￿ ￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿ ￿￿ ￿￿ ￿￿ map are indicative of the water level at the time of well completion. Therefore, current site ￿￿ ￿￿ ￿￿

￿￿ ￿￿ ￿￿ ￿￿ ￿￿ specific conditions may differ due to local or seasonal variations in measured static water levels. ￿￿ ￿￿ ￿￿ ￿￿

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￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿￿￿ ￿￿ ￿￿￿￿ Coordinate locations of water well records were physically obtained in the field, determined

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￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿ through address geocoding, or reported on water well records. Elevation data were either ￿￿ ￿￿￿￿

￿￿ Mud Long obtained from topographic maps or a digital elevation model (DEM). Elevation and location Lake Lake quality control/quality assurance procedures were utilized to refine or remove data where errors

Laketon Bog ￿￿ ￿￿ ￿￿ ￿￿ Mc Calley ￿￿ ￿￿ were readily apparent. Nature Preserve ￿￿￿￿ ￿￿￿￿ ￿￿

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Lake ￿￿ ￿￿ ￿￿ ￿￿ ￿￿￿￿ ￿￿ ￿￿

￿￿￿￿ ￿￿ ￿￿ ￿￿ ￿￿￿￿ ￿￿ In Wabash County well depths 100 feet or less were a priority in mapping the potentiometric ￿￿￿￿ ￿￿ Round ￿￿￿￿ Lake ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ surface. However, portions of Wabash County are lacking in data and/or are covered by deposits Laketon ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ that have limited to non-existent aquifer potential. Therefore, potentiometric surface elevations Lukens contours have not been extended through these areas. There are approximately 535 Lake unconsolidated water well records in the county located that are within the priority depth range. ￿￿￿￿ 13 ￿￿￿￿ ￿￿￿￿

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￿￿￿￿ 15 ￿￿￿￿ ￿￿ ￿￿￿￿ Potentiometric surface elevations range from a high of 850 feet mean sea level (msl) in the ￿￿

«¬ ￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿

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￿￿￿￿ ￿￿ northwest corner of the county, to a low of 640 feet msl in the west-central part of the county ￿￿

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￿￿ ￿￿ along the Wabash River. Generalized groundwater flow direction for Wabash County is towards ￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ major drainage relevant to the basin. Therefore, in the Upper Wabash River Basin, groundwater ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ Ijamsville ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿

￿￿ Servia flow is towards the Wabash River and its major tributaries. These include the Eel River to the

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￿￿ north, the Salamonie River in the east-central part of the county, and the Mississinewa River to

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￿￿￿￿ ￿￿￿￿ ￿￿ the south.

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￿￿￿￿ ￿￿ ￿￿￿￿￿￿ ￿￿￿￿￿￿ ￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿ ￿￿ ￿￿￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ver ￿￿￿￿ Ri ￿￿￿￿ h ￿￿￿￿ ￿￿ ￿￿￿￿ as Salamonie ab Richvalley W Lake

￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ Hillshade Map of Wabash County, Indiana ￿￿ ￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿

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￿￿ ￿￿ ￿￿￿￿ ￿￿

￿￿ ￿￿ ￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ Lincolnville «¬13 ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿

￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿ ￿￿ ￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿ ￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ Asherwood Nature Preserve ￿￿￿￿ 124 ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿ «¬ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ ￿￿ Treaty ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿

￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿

￿￿ ￿￿

Frances Slocum ￿￿

￿￿ ￿￿￿￿ ￿￿

￿￿ ￿￿￿￿ ￿￿ ￿￿ ￿￿

State Recreational ￿￿ ￿￿ ￿￿￿￿ ￿￿

￿￿ ￿￿

￿￿

￿￿

￿￿

￿￿ ￿￿

￿￿ ￿￿￿￿

￿￿ ￿￿

￿￿ ￿￿

￿￿￿￿ ￿￿ ￿￿￿￿ Area ￿￿ ￿￿ ￿￿

￿￿ ￿￿ ￿￿

￿￿ ￿￿ ￿￿

￿￿ ￿￿

￿￿ ￿￿ ￿￿ ￿￿￿￿ ￿￿

￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿ ￿￿

￿￿ ￿￿

￿￿ ￿￿

￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿

￿￿ ￿￿ ￿￿

￿￿

￿￿ ￿￿ ￿￿ ￿￿

￿￿ ￿￿

￿￿

￿￿

￿￿ ￿￿￿￿ ￿￿

￿￿￿￿ ￿￿￿￿ ￿￿￿￿

￿￿ ￿￿

￿￿￿￿ ￿￿ ￿￿

￿￿￿￿ ￿￿￿￿ ￿￿ ￿￿

￿￿￿￿ ￿￿￿￿ ￿￿ ￿￿

￿￿￿￿ ￿￿ 15 ￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿ «¬

￿￿￿￿ ￿￿ ￿￿ ￿￿￿￿ ￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿

￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿

Mississinewa ￿￿￿￿ ￿￿￿￿ ￿￿￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ Lake ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ Gran La Fontaine t Creek

￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿￿￿ Mississinewa EXPLANATION 218 Mount Vernon Lake «¬ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿ ￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿

￿￿ 700 ￿￿

￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿

￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿ ￿￿￿￿

￿￿ ￿￿￿￿

￿￿ ￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿

￿￿ ￿￿￿￿

￿￿

￿￿ ￿￿￿￿ ￿￿

￿￿￿￿ ￿￿￿￿ ￿￿￿￿ ￿￿

￿￿ ￿￿ ￿￿ ￿￿￿￿

￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿

￿￿￿￿ ￿￿ ￿￿￿￿ ￿￿

￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿

￿￿ ￿￿

￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿

￿￿ Somerset ￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ «¬13 ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ¤£24 ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿

￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿

￿￿ ￿￿￿￿￿￿ ￿￿ ￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿

￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿ ￿￿￿￿￿￿ ￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ® ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿

Map Use and Disclaimer Statement ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ Potentiometric Surface Map of the Unconsolidated Aquifers ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ of Wabash County, Indiana ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿ ￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿￿