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Kansas Geological Survey, Ground-water Series 1, originally published in 1974


Geology and Ground-water Resources of Montgomery County, Southeastern Kansas

by Howard G. O'Connor

small image of the cover of the book; aerial photo of Elk City Reservoir by James Elmore, Independence Daily Reporter.

Originally published in 1974 as Kansas Geological Survey Ground-water Series 1. This is, in general, the original text as published. The information has not been updated.

Abstract

Consolidated rocks of Pennsylvanian age underlie all of Montgomery County and are exposed in most of the upland area. Sandstone beds in the Stranger Formation, Stanton Limestone, and Chanute Shale are the most important consolidated-rock aquifers. Locally, wells in the Stranger may yield as much as 20 gallons per minute, the Stanton yields as much as 15 gallons per minute to wells in the southwestern part of the county, and wells in the Chanute may yield as much as 50 gallons per minute. In parts of the county, suitable water for domestic and stock use is obtained from sandstone at depths of 200 to 400 feet. In other parts of the county, ground water may be moderately saline at depths of 50 feet or less.

Fluvial deposits of Quaternary age underlie flood plains and terraces along the stream valleys, and are an important source of ground water. These deposits yield as much as 100 gallons per minute to wells in the Verdigris River valley and from 5 to 50 gallons per minute in other major stream valleys. The water generally is very hard, but is suitable for domestic and stock use except in local areas where excessive concentrations of sulfate, sodium, and chloride are present.

Aquifers in many local areas have been contaminated by brine associated with oil and gas production and by improperly plugged drill holes. The major use of ground water is for domestic and stock supplies. All of the cities use treated surface water, and water districts obtain surface water to serve much of the rural population.

Plate

Plate 1--Geohydrologic map of Montgomery County
Available as an Acrobat PDF file, 6.4 MB

Introduction

This report describes the geology and groundwater resources of Montgomery County, an area of 649 squares miles in southeastern Kansas (fig. 1). The investigation on which this report is based was part of a continuing program of ground-water investigations begun in 1937 by the Kansas Geological Survey and the U.S. Geological Survey, with support from the Division of Environmental Health of the Kansas State Department of Health and the Division of Water Resources of the Kansas State Board of Agriculture. The classification and nomenclature of the stratigraphic units used in this report (table 1) are those of the Kansas Geological Survey and differ somewhat from those of the U.S. Geological Survey.

Figure 1--Index map of Kansas showing area described in this report and areas covered by other online geologic reports, as of Sept. 2010. For additional information, please visit the KGS Geologic Maps of Kansas Page.

Index map of Kansas showing Montgomery County and other bulletins online.

Table 1--Generalized columnar section and water-bearing characteristics.

System Series Stage Group Formation,
or rock unit
Thickness,
in feet
Lithology Water supply1
Quaternary Pleistocene     Alluvium 0-60 Unconsolidated clay, silt, sand, and gravel. Basal part contains 0 to 14 feet of sand and gravel. Yields moderate supplies of water to wells in parts of the Verdigris River valley and in major tributary valleys.
Terrace
deposits
0-38 Yields moderate supplies of water to wells in low terrace deposits. Intermediate and high terrace deposits yield lesser amounts to wells or may be above water table.
Pennsylvanian Upper Pennsylvanian Virgilian Douglas Lawrence
Formation
140 Chiefly olive-gray shale. As much as 30 feet of sandstone in upper part. Thin bed of Haskell Limestone Member at base. Yields very small supplies of water to shallow wells in weathered zones. Sandstone beds generally above water table.
Stranger
Formation
100-175 Gray shale and siltstone, and gray fine-grained sandstone. Thin bed of Westphalia Limestone Member in upper part. Generally yields small to moderate supplies of water to wells in areas underlain by sandstone. Where sandstone beds are absent, yields very small to small supplies to shallow wells in weathered zone.
Missourian Lansing Stanton
Limestone
70-130 Consists of three limestone and two shale members. Limestones include fine-grained dense limestone, oolitic and sandy limestone, and fine-grained to coarsely crystalline limestone. Lower shale member locally includes a black fissile shale. Upper shale contains sandstone beds in outcrops in southern part of county. Generally yields very small supplies of water to wells. Yields very small to small supplies of water to wells in areas underlain by thick limestone beds or shale. In southwestern part of county, yields very small to moderate supplies of water to wells in sandstone.
Vilas Shale 50-120 Chiefly medium-gray shale. Generally yields little or no water to wells except in the shallow zone of weathering.
Plattsburg
Limestone
0-70 Thick gray fine-grained to crystalline limestone in northern part of county. Thin or absent south of Elk River.
Kansas City Bonner Springs
Shale and
Lane Shale
85-150 Gray silty to argillaceous shale.
Iola
Limestone
2-10 Consists of two limestones separated by a black fissile shale containing phosphatic concretions. Lower limestone locally sandy or may be absent. Generally yields little or no water to wells except in the shallow zone of weathering. Yields small supplies to wells locally from black shale.
Chanute
Shale
80-200 Chiefly gray shale and fine-grained sandstone. The Noxie Sandstone Member occurs extensively in the lower part and the Cottage Grove Sandstone Member in the upper part. The middle part contains the Thayer coal bed, one to three thin limestones, and gray shale. Widespread aquifer. Generally yields small to moderate supplies of water to wells from sandstone beds at depths of as much as 400 feet.
Drum
Limestone
0-60 Light-gray fine-grained limestone and light-gray crossbedded very fossiliferous oolitic limestone. Generally yields little or no water to wells except in the shallow zone of weathering
Cherryvale
Shale
0-90 Chiefly bluish-gray shale with flagstones at top in outcrops in northern part of county. Flags increase in abundance southward.
Dennis
Limestone
10-70 Light-gray to bluish-gray limestone, locally sandy or oolitic in upper part. Gray shale and black fissile shale in lower part. Locally contains a 1- to 4-foot thick limestone at base. In northeast area, yields very small to small supplies of water to wells at depths of as much as 200 feet. Elsewhere, generally yields little or no water except in the shallow zone of weathering.
Coffeyville
Formation
200 Chiefly medium-gray shale and siltstone. Upper part locally contains much fine-grained sandstone and several thin coals. Lower beds contain medium- to dark- gray and black shale. The Swope Limestone, 1 to 6 feet of gray limestone, occurs near the middle. Generally yields little or no water to wells from the gray shales, siltstones, and thin limestones. Beds of sandstone and black shales locally yield small supplies of water to wells.
Pleasanton Checkerboard
Limestone
1-14 Consists of two thin limestones separated by gray shale where thickest. Lower limestone is brown-weathering crossbedded coquina. Generally yields little or no water to wells from the gray shales, siltstones, and thin limestones. Beds of sandstone and black shales locally yield small supplies of water to wells.
Seminole
Formation
5-10 Chiefly medium- to dark-gray shale. Locally contains a thin fine-grained sandstone at base.
Middle
Pennsylvanian
Desmoinesian Marmaton Holdenville
Shale
5-25 Gray and bluish-green fossiliferous shale. Generally yields little or no water to wells.
Lenapah
Limestone
7-18 Upper massive limestone and lower nodular bedded limestone separated by a thin gray shale. Yields very small to small supplies of water to wells generally less than 50 feet deep.
Nowata Shale 3-30 Medium- to light-gray shale, locally contains some fine-grained sandstone.
Altamont
Limestone
15-20 Upper and lower light-gray limestone members separated by gray and black fissile shale.
Bandera
Shale
60-150 Gray shale and sandstone.
1In this report, very small supplies refers to yields generally less than 1 gpm, small supplies to 1 to 5 gpm, and moderate supplies to 5 to 100 gpm.

Well and test-hole numbers used in this report give locations according to the U.S. Bureau of Land Management system of land subdivision. The number is composed of township, range, and section numbers, followed by letters that indicate the subdivision of the section in which the well is located. The first letter denotes the quarter section, or 160-acre tract; the second letter denotes the quarter-quarter section, or 40-acre tract; and the third letter, when used, indicates the quarter-quarter-quarter section, or 10-acre tract. The 160-acre, 40-acre, and 10-acre tracts are designated a, b, c, and d in a counter-clockwise direction, beginning in the northeast quarter (fig. 2).

Figure 2--Well-numbering system used in this report.

Letter designation go from largest to smallest while quarter calls go from smallest to largest; thus 35baa (a = NE, b = NW, c = SW, d = SE) is the same as as NE NE NW sec. 35.

Ground Water in Consolidated Rocks

Ground-water supplies in the consolidated rocks in parts of Montgomery County are inadequate or are of poor chemical quality for domestic and livestock use; however, in other parts of the county, sandstone aquifers yield as much as 50 gpm (gallons per minute) of good quality water to wells.

Sandstone beds in the Stranger Formation, Stanton Limestone, and Chanute Shale are the most important consolidated-rock aquifers (table 1). Locally, the Stranger Formation contains more than 100 feet of sandstone and siltstone, and well yields of as much as 20 gpm of hard but otherwise good quality water for domestic and stock use can be obtained (table 2). In the southwestern part of Montgomery County, as much as 40 feet of sandstone in the upper and middle parts of the Stanton yields 1/2 to 15 gpm of good to poor quality water to wells.

Table 2--Chemical analyses of water from selected wells, test holes, and springs. [Dissolved constituents and hardness given in milligrams per liter. Analyses by Kansas State Department of Health.]

Well
number
Sample
id
number
Depth of
well below
land surface
(feet)
Geologic
source1
Date of
collection
Temp.
(°C)
Dissolved
solids
(residue
at 180°C)
Dissolved
silica
(SiO2)
Total
iron
(Fe)
Total
manganese
(Mn)
Dissolved
calcium
(Ca)
Dissolved
magnesium
(Mg)
Sodium and
potassium
(Na+K)
Bicarbonate
(HCO3)
Dissolved
sulfate
(SO4)
Dissolved
chloride
(Cl)
Dissolved
fluoride
(F)
Dissolved
nitrate
(NO3)
Hardness3
as CO3
Specific
conductance
(micromhos
at 25°C)
pH
Calcium,
magnesium
Non-
carbonate
31-15E-9bd 1 Spring Stanton Ls 5-2-1960   306 6.5 0.06 0.09 100 5.7 6.7 307 16 15 0.1 3.5 280 26 520  
31-15E-26ba 2 61 Lane and
Bonner Springs Sh
6-2-1959   908 12 .74 .00 64 19 260 516 140 150 1.0 16 240 0 1,580  
31-15E-32dd 3 120 Chanute Sh 5-2-1960   1,730 10 .52 .07 55 15 610 448 20 800 2.0 2.4 200 0 3,250  
31-16E-5bbb 4 22 Alluvium 5-2-1960   1,250 12 .22 .12 210 54 110 359 450 65 .2 170 740 450 1,890  
31-16E-20dad 5 25 Terrace dep 5-2-1960   530 14 .09 .00 110 20 42 276 170 10 .3 26 350 130 825  
31-16E-30ab 6 105 Chanute Sh 5-5-1960   183 17 .07 .12 31 7.9 22 112 6.2 38 .1 5.8 110 18 315  
32-13E-26bb 7 56 Stranger Fm 6-2-1959   287 14 .14 .00 66 13 11 163 86 8.0 .1 8.0 220 84 455  
32-13E-26bb 8 56 Stranger Fm 5-14-1968   267 12 .06 .00 62 10 13 149 81 9.0 .2 7.1 200 74 390 7.2
32-14E-14cb 9 28 Alluvium 5-5-1960   400 19 .23 .78 120 6.9 12 314 36 6.0 .1 49 320 60 660  
32-14E-23bab 10   Chanute(?) Sh 5-14-1963   1,290 5.4 1.7 .14 8.0 3.9 500 5442 53 420 .6 1.5 36 0 2,140 8.9
32-15E-33abb 11 80 Chanute Sh 4-24-1963   2,220 15 .09 .81 500 64 93 327 1,200 61 .5 140 1,500 1,200 2,580  
32-16E-7ab 12 90 Chanute Sh 5-5-1960   311 25 9.1 .27 31 11 57 143 48 40 .2 28 120 5 515  
32-16E-26dc 13 168 Coffeyville Fm 4-25-1963   464 10 .13 .10 86 32 44 410 74 8.0 .4 8.4 350 10 800  
32-16E-29dd 14 23 Chanute Sh 6-3-1959   1,170 12 .38 .35 150 52 150 207 630 62 .3 11 600 420 1,700  
32-17E-9bb 15 79 Cherryvale(?) Sh 4-24-1963   574 10 3.8 .10 110 25 57 346 160 37 .1 .4 390 100 940  
32-17E-31dbb 16 71 Cherryvale(?) Sh 4-24-1963 15.0 342 7.0 2.3 .12 100 12 10 327 36 11 .1 .4 310 41 600  
33-13E-36ba 17 140 Stanton Ls 6-3-1959   3,890 10 .19 .00 27 12 1,500 510 20 2,100     120 0 7,390  
33-13E-36ca 18 25 Stranger Fm 6-3-1959   737 11 .14 .00 120 43 99 524 110 87 .1 9.3 460 34 1,280  
33-14E-14ab 19 33 Stanton Ls 6-3-1959 14.5 246 6.0 .08 .00 59 11 7.4 129 77 6.0 .2 16 190 86 425  
33-14E-14bb 20 40 Stanton Ls 6-3-1959   932 13 .03 .00 180 37 72 316 400 51 .3 23 610 350 1,400  
33-14E-34ad 21 80 Stanton Ls 6-3-1959   1,750 14 .66 .20 240 120 160 603 810 63 .3 35 1,100 620 2,450  
33-15E-8dc 22 15 Vilas and Lane Sh 6-3-1959   2,920 7.0 .16 .00 500 140 280 256 1,100 730 .4 53 1,800 1,600 4,500  
33-15E-27cc 23 74 Chanute Sh 4-25-1963 15.5 2,170 9.5 1.9 .31 290 170 150 378 1,300 16 .6 1.1 1,400 1,100 2,550  
33-16E-7bc 24 125 Chanute Sh 6-3-1959   3,690 24 .30 .00 520 240 280 464 2,200 91 .5 71 2,300 1,900 4,240  
33-16E-7dc 25 44 Chanute Sh 5-2-1960 14.0 474 11 3.9 .92 68 33 44 217 200 11 .3 4.4 300 130 750  
33-16E-20bb 26 90 Chanute Sh 6-3-1959   838 17 3.9 .46 100 56 140 664 66 130 .1 1.3 490 0 1,490  
33-16E-30bc 27 175 Chanute Sh 6-3-1959 15.5 680 14 3.8 .00 41 21 170 376 230 12 .4 1.8 190 0 1,100  
33-16E-32bd 28 59 Chanute Sh 5-3-1960   175 25 .14 .00 31 7.4 12 107 12 9.0 .1 26 110 20 255  
33-17E-15cd 29 20 Coffeyville Fm 4-25-1963   2,880 9.0 .13 .11 230 180 410 412 1,600 77 .7 190 1,300 990 3,550  
34-13E-13ba 30 140 Stanton Ls 6-3-1959   3,590 7.0 .22 .00 40 17 1,400 466 28 1,900 1.9 2.0 170 0 6,880  
34-14E-11ddd 31 85 Stanton Ls 5-4-1960   1,300 10 .07 .00 230 45 140 386 550 91 .5 53 760 440 1,920  
34-14E-12dd 32 Spring Stanton Ls 6-3-1959 15.0 221 6.0 .03 .00 64 6.9 8.3 207 14 9.0 .1 11 190 18 410  
34-14E-16ab 33 65 Stanton Ls 4-24-1963   3,740 12 23 .48 500 340 180 527 2,400 49 .7 1.1 2,600 2,200 4,010  
34-14E-25da 34 74 Stanton Ls 4-25-1963   529 12 .05 .10 100 38 38 390 120 25 .2 1.9 410 90 860  
34-14E-36dd 35 175 Chanute Sh 5-4-1960   786 11 .08 .00 24 7.3 270 413 120 120 1.6 3.4 90 0 1,320  
34-15E-15cb 36 65 Chanute Sh 6-3-1959   204 22 .66 .00 39 6.5 16 124 4.1 13 .1 42 120 22 335  
34-15E-25da 37 30 Chanute Sh 5-3-1960 15.0 1,690 16 .80 3.2 250 49 300 702 420 310 .3 4.1 820 240 2,620  
34-15E-26da 38 40 Chanute Sh 5-3-1960   302 25 .26 .11 53 11 32 184 42 21 .1 27 180 25 505  
34-16E-16aa 39 65 Chanute Sh 5-3-1960   224 19 .08 .08 36 9.3 22 116 56 6.0 .1 19 130 34 360  
34-16E-16dc 40 Spring Chanute Sh 5-3-1960 13.0 139 18 .04 .00 27 5.0 11 101 14 4.0 .1 10 88 5 220  
34-16E-17ab 41 50 Chanute Sh 5-3-1960 15.0 261 16 .21 .00 48 23 17 278 9.1 7.0 .6 3.6 210 0 445  
34-16E-30bc 42 29 Chanute Sh 5-3-1960   486 7.5 .07 .00 110 23 20 273 91 43 .1 53 380 160 860  
34-17E-15cc 43 31 Coffeyville(?) Fm 4-25-1963 14.5 7,160 9.5 .11 .10 520 850 480 504 4,400 510 1.1 170 4,800 4,400 7,350  
34-17E-19cd 44 Spring Terrace dep 5-4-1960 15.0 499 13 .06 .00 120 15 31 311 86 53 .2 24 370 120 880  
34-17E-28bb 45 32 Checkerboard Ls
and Seminole(?) Fm
5-4-1960   1,210 17 1.0 .00 180 52 170 334 400 230 .4 2.1 650 380 1,920  
34-17E-34aa 46 23 Altamont Ls 4-25-1963 13.5 1,110 9.0 .05 .00 210 53 69 284 310 140 .1 180 750 520 1,690  
35-14E-1ab 47 190 Chanute Sh 5-4-1960   644 8.0 .39 .12 110 20 82 190 160 120 .1 43 360 200 1,120  
35-14E-6dcc 48 59 Stanton Ls 5-4-1960 14.5 1,210 13 .12 .12 87 53 270 539 440 81 1.7 5.8 440 0 1,850  
35-14E-9dd 49 265 Chanute Sh 5-4-1960 18.0 1,550 12 6.3 .38 20 9.3 580 573 35 600 2.2 8.0 88 0 2,750  
35-14E-16dba 50 255 Chanute Sh 5-4-1960   1,780 8.5 .09 .00 5.8 7.2 710 832 .0 630 4.6 2.8 44 0 3,250  
35-15E-1add 51 35 Chanute Sh 6-3-1959 14.5 361 12 .17 .00 94 12 17 261 54 27 .1 16 280 70 650  
35-15E-2ba 52 151 Chanute Sh 6-3-1959 16.0 533 20 .78 .10 81 34 59 354 140 24 .2 2.1 340 52 900  
35-16E-6ba 53 35 Chanute Sh 5-3-1960   269 8.5 .07 .10 76 9.4 11 256 29 7.0 .1 2.5 230 19 465  
35-17E-10ba 54 Spring Lenapah Ls 4-25-1963   305 7.5 .06 .06 93 7.8 13 296 21 12 .4 5.3 260 22 530  
Kansas State Board of Health (1973) recommended
maximum concentration for drinking water
500   .3 .05         250 250 1.5 45        
1 dep, deposits; Fm, Formation; Ls, Limestone; Sh, Shale.
2 Includes 46 mg/l carbonate.
3 The classification for hardness used in this report is as follows: 0-60, soft; 61-120, moderately hard; 121-180, hard; more than 180, very hard.

The Chanute Shale ranges in thickness from about 80 feet in the northern part of Montgomery County to about 200 feet in the southern part. It contains two extensive sandstone members-the Cottage Grove in the upper part and the Noxie in the lower part. Well yields range from less than 1 gpm to as much as 50 gpm. The chemical quality of water supplies obtained from these sandstones ranges from good to poor for stock and domestic use. Some wells in the Cottage Grove Member and the Noxie Member obtain very hard water of the calcium and magnesium sulfate type, whereas other wells obtain much softer water having sodium chloride and sodium bicarbonate as the principal constituents (fig. 3). About one-fourth of the water samples collected from wells and springs obtaining water from the Chanute have dissolved-solids concentrations of less than 300 mg/l (milligrams per liter); this water generally is of good quality for stock and domestic use.

Figure 3--Modified Piper diagram showing grouping of analyses of water from wells. Numbers by symbols are sample-identification numbers from table 2.

Chemical analyses plotted on modified Piper diagram.

A few wells obtain water from sandstone beds in the Coffeyville and Seminole Formations in eastern Montgomery County. Locally, water from the Coffeyville, even at shallow depths, may be of poor quality and unsuitable for domestic or stock use because of large concentrations of sulfate (table 2). No wells were inventoried that obtained water supplies from sandstones in the Nowata or Bandera Shales, although small water supplies might be obtainable from these units east of the Verdigris River and south of Claymore Creek in southeastern Montgomery County.

Most limestone units at shallow depths in Montgomery County will yield small supplies of ground water to large-diameter wells in the zone of weathering during periods of normal or above normal precipitation. The thick limestone reefs or banks of the Stanton and Plattsburg Limestones in northwestern Montgomery County and the Drum Limestone in the Independence area are unreliable sources of water for wells. A few wells obtain domestic and stock water supplies at depths of 200 feet or less from the Dennis Limestone in the northern part of T.31 S., R.17 E. Limestone aquifers generally yield hard to very hard water of the calcium bicarbonate type. Locally, the concentration of sulfate may be excessive for domestic use.

The shale units in Montgomery County generally yield little water to wells. Shallow large-diameter wells constructed in weathered shale may yield 100 to 1,000 gallons per day, but may be dry part of the time. Black or dark-gray shales commonly contain plant and other carbonaceous material and associated iron sulfides. Water from shallow wells in these shales may be very hard and contain so much sulfate that it is not suitable for either domestic or stock use.

The deepest known fresh (less than 1,000 mg/l dissolved solids) to slightly saline (1,000 to 3,000 mg/l dissolved solids) water supplies in the county are from sandstone in the Chanute Shale in the southwestern part of the county at depths of 200 to 400 feet below land surface, and from the Dennis Limestone and Coffeyville Formation in the northeastern part at depths of 100 to about 250 feet. Locally, in southeastern Montgomery County, ground water at depths of less than 50 feet is moderately saline (3,000 to 10,000 mg/l dissolved solids). Oil has been reported at depths of less than 50 feet in the vicinity of Coffeyville, and the water associated with the oil is not suitable for domestic use. Throughout the county, rocks older than the Bandera Shale yield saline water having dissolved-solids concentrations greater than 3,000 mg/l. These rocks commonly contain water having 10,000 to 200,000 mg/l dissolved solids. Although shallow consolidated-rock aquifers may contain large concentrations of sulfate locally, the chloride concentration is normally low.

Aquifers in many local areas have been contaminated by brine associated with oil and gas production and by improperly plugged abandoned drill holes. In these areas, the contamination of fresh ground water is indicated by the increased amounts of sodium chloride in relation to other constituents. Most of the more than 11,000 holes drilled for oil and gas in Montgomery County were drilled prior to the enactment of legislation in 1934 regulating the drilling, casing, and plugging of wells and the disposal of produced brine to protect the fresh and usable water resources. Improperly plugged wells in local areas are a continuing source of contamination.

Water levels in the consolidated-rock aquifers fluctuate in response to natural discharge and recharge of water and to pumping by wells. Hydrographs for three wells tapping consolidated-rock aquifers are shown on figure 4. Fluctuations of water levels in wells tapping consolidated-rock aquifers in highly dissected topography, such as along a bluff of a stream valley, or in wells tapping aquifers of poor water-yielding characteristics, such as some of the shale units, generally are relatively large. Fluctuations of water levels in wells tapping the better aquifers, or aquifers that are not highly dissected, generally are small.

Figure 4--Hydrographs for four consolidated wells.

Water level readings for Stranger Fm, Chanute Sh, Alluvium, and undifferentiated Bonner Springs and Lane shales.

Ground Water in Unconsolidated Deposits

Fluvial deposits of clay, silt, sand, and gravel, which form and underlie the flood plains and low terraces of stream valleys, are important sources of ground water. Information obtained from wells and test holes (geohydrologic map) indicates that the thickness of alluvium commonly ranges from about 10 to 60 feet. Four geologic sections (fig. 5) illustrate the range in thickness of the alluvium and the low-terrace deposits, show the position of the water table and the thickness of saturated deposits, and indicate that the water table slopes toward the streams and that ground water is discharged to the streams. During high stages of the streams, when surface water is above the level of the adjacent water table, water in streams infiltrates and recharges the aquifer. Yields of wells in the alluvium and low-terrace deposits may be as much as 100 gpm in the Verdigris River valley, and may range from 5 to 50 gpm in other major stream valleys.

Figure 5--Geologic sections. Traces of the sections are also shown on the geohydrologic map. [This figure is also available as an Acrobat PDF file (432 kb).]

Three cross sections.

The chemical quality of water from the alluvium and low-terrace deposits ranges from good to poor for domestic and stock use. These aquifers generally yield very hard water of the calcium bicarbonate type that is low in concentrations of chloride, but locally may contain appreciable concentrations of sulfate. In some areas, however, high concentrations of sodium and chloride result from contamination associated with past oil and gas exploration and production.

Water levels in test holes in the alluvium ranged from about 3 to 22 feet below land surface in 1961. A water-level fluctuation of 13 feet during 1961-69 is shown by the hydrograph for observation well 34-17E-31ac in the alluvium near Coffeyville (fig. 4). Water-level changes of 20 feet or more in areas not affected by pumping probably should be expected in the alluvium of the Verdigris River valley during a cycle of wet and dry years.

The older fluvial deposits that occur as dissected and discontinuous terraces 20 to 100 feet above the flood plain may contain a thin saturated section or may be above the water table.

Ground-water Development

The largest development of ground water in the county is for livestock and domestic use. In some areas, aquifers have only very small supplies of ground water or have hard water of poor quality. In other areas, aquifers have been contaminated by brine as a result of improper drilling, casing, and plugging of oil and gas wells and the improper handling of brines in the early years of oil and gas exploration. Since 1960, therefore, an effort has been made to expand rural water-distribution systems using water purchased from larger cities; all cities in Montgomery County utilize treated surface water for their water supplies. The trend toward public-water supplies to serve rural areas probably will continue even though some areas served by rural water districts have ground-water supplies of good quality.

No irrigation developments utilize ground water and only a few industries have developed small ground-water supplies. Some ground water from shallow wells is used in oil-field secondary recovery projects.

Selected References

Abernathy, G. E., 1940, Oil and gas in Montgomery County, Kansas: Kansas Geol. Survey Bull. 31, 29 p.

Goebel, E. D., 1962, The occurrence of oil and gas in Wilson and Montgomery Counties, Kansas: Kansas Geol. Society, 27th Field Conf. Guidebook, p. 134-137.

Harbaugh, J. W., 1962, Geologic guide to Pennsylvanian marine banks, southeast Kansas: Kansas Geol. Society, 27th Field Conf. Guidebook, p. 13-67.

Hem, J. D., 1970, Study and interpretation of the chemical characteristics of natural water: U.S. Geol. Survey Water-Supply Paper 1473, 2d ed., 363 p.

Kansas State Board of Health, 1973, Water quality criteria for interstate and intrastate waters of Kansas: Kansas State Board of Health Regulations 28-16-28, 5 p.

Kansas Water Resources Board, 1960, Preliminary appraisal of Kansas water problems, sec. 5, Walnut-Verdigris Unit: Kansas Water Resources Board, State Water Plan Studies, pt. A, 160 p.

Latta, B. F., 1963, Fresh water pollution hazards related to the petroleum industry in Kansas: Kansas Acad. Sci. Trans., v. 66, no. 1, p. 25-33.

O'Connor, H. G., 1962, A summary of the geology of Montgomery County, Kansas: Kansas Geol. Society, 27th Field Conf. Guidebook, p. 149-158.

Schrader, F. C., 1908, Independence folio, Kansas: U.S. Geol. Survey Geol. Atlas, Folio 159, 17 p.


Kansas Geological Survey, Montgomery County, Kansas
Placed on web Sept. 7, 2010; originally published in Sept. 1974.
Comments to webadmin@kgs.ku.edu
The URL for this page is http://www.kgs.ku.edu/Publications/Bulletins/GW1/index.html