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Kansas Geological Survey, Current Research in Earth Sciences, Bulletin 258, part 3
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Methodology

Water samples were collected monthly from nine public water-supply wells located within the transition zone in Crawford and Cherokee counties in southeast Kansas (fig. 1; table 1). Newer wells tapping supplies in the Ozark Plateaus aquifer system are steel-cased through the Pennsylvanian to prevent fluids and natural gas from entering the well in the upper part of the boreholes. Below the casing and down to total depth, wells are completed as open boreholes from which water is produced. Five of the monitored wells tap supplies in the Ozark aquifer, and three tap supplies in both the Springfield Plateau and the Ozark aquifers (referred to in this paper as multi-aquifer wells). Of the three multi-aquifer wells, the older Weir city well potentially taps minor sources of water in the overlying Pennsylvanian rocks in addition to the Springfield Plateau and Ozark aquifers.

Water samples were collected in 500-mL polyethylene bottles after the well had been pumped for at least 15 minutes, or after the specific conductance and temperature had stabilized. If the well was running on arrival at the site, the water-supply operator was queried to obtain an estimate of how long the well had been pumping. Most of the time the well had been running for at least one hour prior to sampling. Some of the wells could not be sampled every month because of restrictions on the amount of water that could be pumped or mechanical problems.

Temperature, pH, and specific conductance were measured at the time of sampling. Samples were kept in an ice-chest after collection and later transferred to a refrigerator in the Analytical Services laboratory at the Kansas Geological Survey (KGS).

Water-quality pumping tests were conducted to assess changes in the chemistry of produced water over a single pumping period. Well 8 in the Pittsburg well field was selected for testing because it had been sampled monthly in the previous phase of this research. It is located on the western side of the regional cone of depression in the Ozark aquifer potentiometric surface (fig. 2) and structurally near the crest of the Pittsburg anticline (fig. 3; Macfarlane and Hathaway, 1987). Well 8 is cased through the overlying Springfield Plateau aquifer and was completed as an open borehole from the Jefferson City Dolomite into the upper part of the Gasconade Dolomite (table 3). Water is produced from the well by a turbine pump at the rate 1,875 gal/minute (118 L/second).

In 2008, tests were conducted in late June near the beginning of what is normally a period of high water demand and in early September just after the time of peak demand. The monitoring well hydrograph in fig. 5 shows that the elevation of the potentiometric surface is generally higher during low pumping-stress periods than it is during high pumping-stress conditions. The June test duration was 50.7 hours, during which 26 water samples were collected, and the September test duration was 51.8 hours, during which 28 samples were collected. The interval between samplings varied from 15 minutes to 8.8 hours in the June test and from 30 minutes to 3 hours in the September test.

Figure 5--(A) Aerial photograph showing the location of the observation well (from which the hydrograph in B was generated) in relation to wells 8 and 10 in the city of Pittsburg, Kansas, field. (B) Hydrograph of the monitoring well completed in the Ozark aquifer in the Pittsburg well field showing depth to water from land surface. The arrows indicate the approximate start time of each chemical-quality pumping test.

Aerial photo of observation well and depth to water from May to October.

Samples were refrigerated until processed in the KGS laboratory. Specific conductance and pH were measured after the samples had equilibrated to room temperature. Samples were then analyzed for calcium, magnesium, strontium, sodium, potassium, bicarbonate, sulfate, and chloride. Anion analyses were performed using ion chromatography with a Dionex ICS-3000 and cation concentrations were measured using a Jarrel-Ash ICP. Prior to analysis, samples processed for the Dionex and the Jarrel-Ash were passed through 0.2-micron and 0.45-micron filters, respectively. Bicarbonate was determined using an automated titrimeter. Most of the analytical results are within 2% of electrical balance based on milliequivalent/liter (meq/L) values, and all of the analyses are within 5% of balance. TDS concentration was calculated by summing the major and minor constituent concentrations. In the TDS calculation, the bicarbonate concentration was multiplied by 49.17% to approximate the amount of carbonate that would be left in the residual solids after evaporating to dryness. The analytical results are in tables 4-15. Water-type classification is based on whether the percent meq/L contributions of individual dissolved cations and anions exceed 50% of the total meq/L concentration of cations or anions. Waters in which none of the constituent concentrations exceed 50% of the total cations or anions were classified as mixed.

Table 4--Water type and TDS concentration range for each of the nine wells sampled monthly from 2006-08.

Water Supply Well Water Type TDS
Concentration
Range (mg/L)
Number
of
Samples
Cherokee RWD 3 well 1 Sodium-chloride 541-644 20
Columbus well 4 Mixed cation-bicarbonate to sodium-bicarbonate 466-617 19
Crawford Consolidated RWD 1 well 2 Mixed cation-mixed anion 663-721 20
Crawford RWD 4 well 3 Mixed cation-bicarbonate 478-534 20
Crawford RWD 5 well 1 Mixed cation-bicarbonate 516-566 20
Girard 3 Mixed cation-mixed anion 639-674 20
Pittsburg 8 Mixed cation-bicarbonate 481-551 16
Pittsburg 10 Mixed cation-bicarbonate 516-545 3
Weir Mixed cation-bicarbonate 396-497 18

Table 5--Chemical analyses of the monthly 2006-08 samples collected from Cherokee RWD 3 well 1.

Date
Sampled
Sp. Con.
(µS/cm)
pH TDS
(mg/L)
Ca
(mg/L)
Mg
(mg/L)
Na
(mg/L)
K
(mg/L)
Sr
(mg/L)
HCO3
(mg/L)
SO4
(mg/L)
Cl
(mg/L)
4/13/2006 1081 7.60 590 44.4 21.9 136 7.5 1.32 220 39.6 211
5/15/2006 1040 7.40 572 46.3 22.2 134 6.4 1.26 216 45.5 199
6/15/2006 1010 7.45 559 45.9 22.3 130 6.2 1.21 212 43.2 195
7/13/2006 1067 7.83 578 45.5 22.2 136 6.8 1.32 221 36.8 209
8/15/2006 1140 8.00 592 44.1 21.8 142 8.3 1.38 224 42.7 210
9/19/2006 1052 8.10 570 45.7 22.1 129 5.6 1.19 219 44.8 203
10/16/2006 1021 7.52 562 46.8 22.5 133 6.0 1.31 209 40.0 198
11/21/2006 1051 7.80 583 46.1 22.7 134 6.3 1.27 214 46.8 209
12/19/2006 1011 8.00 564 46.5 22.6 129 5.8 1.19 213 42.9 200
1/26/2007 1072 7.80 598 45.3 22.1 144 7.1 1.36 223 38.4 219
3/20/2007 1137 7.90 618 46.0 22.5 149 6.7 1.30 239 47.2 217
4/1/2007 1159 7.80 641 44.5 22.3 161 7.2 1.44 263 42.8 222
5/15/2007 1163 7.95 644 47.2 22.8 152 7.3 1.50 243 47.5 235
6/1/2007 1036 7.80 573 46.8 22.3 133 6.1 1.28 215 43.4 205
8/1/2007 1031 7.34 558 47.8 22.8 129 6.0 1.24 210 44.5 193
10/1/2007 1085 7.65 591 47.5 22.5 137 6.8 1.37 224 42.7 211
12/1/2007 1145 7.90 545 49.5 23.4 129 6.0 1.23 211 31.9 189.
1/04/2008 931 7.40 585 45.3 21.9 138 6.6 1.33 233 47.3 200
1/25/2008 1015 7.41 571 46.8 22.7 131 6.1 1.25 222 41.9 201
2/28/2008 1044 7.29 541 47.6 22.7 136 6.4 1.32 176 34.2 195

Table 6--Chemical analyses of the monthly 2006-08 samples collected from Columbus well 4.

Date
Sampled
Sp. Con.
(µS/cm)
pH TDS
(mg/L)
Ca
(mg/L)
Mg
(mg/L)
Na
(mg/L)
K
(mg/L)
Sr
(mg/L)
HCO3
(mg/L)
SO4
(mg/L)
Cl
(mg/L)
4/13/2006 828 7.73 487 48.3 24.6 93.5 6.6 1.37 356 57.6 63.2
5/15/2006 796 7.62 491 49.1 24.8 91.8 5.7 1.35 361 69.7 59.1
6/15/2006 789 7.66 477 48.5 24.2 91.4 6.0 1.36 362 53.3 62.5
8/15/2006 966 8.00 574 53.3 26.9 122 7.3 1.50 350 52.6 126
9/19/2006 872 7.85 519 50.6 24.9 102 5.8 1.45 357 61.8 85.1
10/16/2006 904 7.52 536 53.2 26.3 110 6.2 1.53 354 59.1 93.2
11/21/2006 982 7.70 579 52.8 26.4 122 7.0 1.49 361 62.7 117
12/19/2006 726 7.65 473 47.9 25.0 91.8 5.5 1.32 363 46.9 64.4
1/26/2007 866 7.85 512 50.5 25.1 104 6.5 1.40 364 46.5 86.5
3/19/2007 886 7.95 496 51.5 24.9 97 5.7 1.30 366 55.5 69.1
4/1/2007 1037 7.80 594 54.8 27.0 127 6.6 1.59 356 54.5 136
6/1/2007 815 7.70 470 50.1 24.9 91.0 5.2 1.38 362 47.0 61.4
8/1/2007 980 7.20 573 53.6 25.7 121 7.0 1.54 361 66.3 108
10/1/2007 1096 7.56 617 57.4 27.5 134 7.6 1.65 353 62.3 141
12/1/2007 1102 7.58 612 55.0 27.2 137 7.0 1.59 364 54.6 140
1/04/2008 787 7.45 530 52.0 25.4 111 6.8 1.48 362 54.7 88.8
1/25/2008 776 7.62 466 48.7 24.6 94.4 5.7 1.37 374 39.3 56.0
2/28/2008 806 7.42 469 50.8 24.8 94.9 6.2 1.44 359 43.0 59.4
5/15/2008 829 7.75 484 51.6 25.3 93.3 5.4 1.41 361 55.1 62.3

Table 7--Chemical analyses of the monthly 2006-08 samples collected from Crawford RWD 4 well 3.

Date
Sampled
Sp. Con.
(µS/cm)
pH TDS
(mg/L)
Ca
(mg/L)
Mg
(mg/L)
Na
(mg/L)
K
(mg/L)
Sr
(mg/L)
HCO3
(mg/L)
SO4
(mg/L)
Cl
(mg/L)
4/13/2006 917 7.32 511 64.9 31.0 78.1 9.9 1.15 337 72.9 86.2
5/15/2006 907 7.41 534 68.4 32.2 80.6 7.7 1.22 332 80.2 99.3
6/15/2006 886 7.25 508 67.8 31.7 79.9 6.7 1.20 329 80.0 78.4
7/13/2006 905 7.46 506 64.0 30.5 76.0 7.1 1.13 335 79.8 82.0
8/15/2006 910 7.75 514 65.7 32.1 78.0 6.6 1.14 329 83.2 84.8
9/19/2006 919 7.95 522 66.5 31.6 78.5 5.7 1.17 333 88.8 85.1
10/16/2006 892 7.53 505 67.6 31.9 79.5 5.6 1.19 327 76.6 80.9
11/20/2006 918 7.45 524 66.2 31.5 78.4 5.7 1.17 333 88.7 87.7
12/18/2006 912 7.55 518 67.2 33.0 79.2 6.3 1.17 335 81.9 83.7
1/25/2007 901 7.45 517 68.3 31.9 80.5 6.5 1.19 330 79.5 85.6
3/19/2007 916 7.60 519 68.1 31.2 79.6 6.4 1.10 334 80.9 86.8
4/1/2007 914 7.50 511 66.8 31.5 77.8 6.0 1.21 334 75.5 86.7
5/14/2007 958 7.45 512 67.7 31.5 78.8 6.2 1.22 331 77.2 85.4
6/1/2007 908 7.45 519 67.3 30.8 78.7 6.3 1.19 331 85.5 85.6
8/1/2007 907 6.97 518 68.3 31.5 80.5 6.7 1.22 334 83.0 81.5
10/1/2007 1319 7.26 517 68.2 31.4 80.4 6.6 1.21 337 79.4 83.1
12/1/2007 925 7.21 504 71.2 33.6 83.2 6.7 1.26 336 60.8 81.4
1/04/2008 773 7.13 515 68.0 29.7 80.1 6.5 1.18 334 83.6 80.4
1/25/2008 875 7.16 513 67.8 31.0 80.1 6.5 1.20 331 77.8 84.5
2/27/2008 893 6.82 478 67.9 31.5 80.4 6.7 1.21 337 58.9 64.7

Table 8--Chemical analyses of the monthly 2006-08 samples collected from Crawford RWD 5 well 1.

Date
Sampled
Sp. Con.
(µS/cm)
pH TDS
(mg/L)
Ca
(mg/L)
Mg
(mg/L)
Na
(mg/L)
K
(mg/L)
Sr
(mg/L)
HCO3
(mg/L)
SO4
(mg/L)
Cl
(mg/L)
4/13/2006 680 7.62 545 46.9 21.0 66.7 4.3 0.64 291 26.7 69.7
5/15/2006 665 7.54 531 47.1 20.8 63.7 4.3 0.63 287 32.1 65.0
6/15/2006 660 7.40 538 46.9 21.0 65.5 4.0 0.64 290 26.1 73.4
7/13/2006 680 7.70 516 48.4 21.3 59.7 3.8 0.62 275 29.4 67.3
8/15/2006 651 7.90 520 47.1 21.2 61.0 4.2 0.61 279 27.9 68.5
9/19/2006 709 7.95 538 47.0 20.7 64.2 3.4 0.63 293 32.0 67.1
10/16/2006 662 7.42 523 49.4 21.5 61.1 3.2 0.63 279 31.3 66.8
11/20/2006 692 7.60 556 48.0 21.6 69.3 3.9 0.66 296 30.8 74.7
12/18/2006 682 7.80 540 46.4 21.0 66.9 4.0 0.64 295 29.2 66.3
1/25/2007 684 7.65 544 47.0 21.7 68.5 4.0 0.64 296 18.6 77.2
3/19/2007 691 7.80 541 47.1 20.9 66.8 4.1 0.60 293 31.4 66.8
4/1/2007 675 7.60 525 49.0 21.9 62.3 3.6 0.64 286 22.4 69.0
5/14/2007 705 7.75 535 48.4 21.2 67.6 3.9 0.67 285 31.1 67.6
6/1/2007 694 8.00 541 49.2 21.6 70.7 4.0 0.69 296 19.2 70.6
8/1/2007 685 7.16 546 48.0 21.1 69.6 4.2 0.68 297 31.1 64.2
10/1/2007 686 7.45 566 48.9 22.4 65.9 3.9 0.64 319 29.5 65.6
12/1/2007 692 7.51 534 49.7 21.7 69.3 4.1 0.68 293 22.5 63.4
1/04/2008 579 7.22 525 48.0 20.9 65.7 3.8 0.65 285 29.1 62.9
1/25/2008 654 7.28 527 48.5 21.4 65.8 3.8 0.66 292 22.9 63.4
2/27/2008 660 7.10 522 48.4 21.3 64.0 4.0 0.64 290 22.8 60.9

Table 9--Chemical analyses of the monthly 2006-08 samples collected from Crawford Consolidated RWD 1 well 2.

Date Sampled Sp. Con.
(µS/cm)
pH TDS
(mg/L)
Ca
(mg/L)
Mg
(mg/L)
Na
(mg/L)
K
(mg/L)
Sr
(mg/L)
HCO3
(mg/L)
SO4
(mg/L)
Cl
(mg/L)
4/13/2006 1247 6.97 684 74.8 34.8 130 6.1 1.51 331 97.6 176
5/15/2006 1247 7.06 686 76.1 35.2 128 7.4 1.48 323 99.9 178
6/15/2006 1248 7.24 663 75.8 35.3 130 7.9 1.49 291 89.8 179
7/13/2006 1233 7.31 689 75.3 35.2 129 7.5 1.48 334 91.1 184
8/15/2006 1188 7.50 677 75.3 34.6 128 6.8 1.47 326 89.3 181
9/19/2006 1229 7.50 688 74.3 34.8 127 6.7 1.46 325 106 177
10/16/2006 1211 7.24 676 75.8 35.5 129 6.8 1.49 323 92.1 176
11/20/2006 1250 7.30 679 74.0 34.5 127 6.9 1.45 326 96.5 178
12/18/2006 1136 7.45 708 76.6 35.4 131 7.0 1.50 330 102 191
1/25/2007 1223 7.30 682 75.6 34.6 130 7.4 1.45 324 90.5 183
3/19/2007 1239 7.45 684 77.0 34.3 130 7.2 1.50 330 97.0 174
4/1/2007 1255 7.20 721 77.0 35.3 131 7.1 1.54 334 109 195
5/14/2007 1270 7.35 694 76.7 35.3 132 7.0 1.55 321 92.9 190
6/1/2007 1137 7.35 680 77.6 35.1 132 7.1 1.56 328 89.4 176
8/1/2007 1225 6.87 695 77.6 35.0 132 7.4 1.57 334 101 175
10/1/2007 1245 6.93 681 74.6 34.1 125 7.0 1.49 327 97.8 180
12/1/2007 1261 7.18 672 78.2 36.0 132 7.4 1.57 336 74.7 176
1/04/2008 1055 7.09 676 77.6 35.6 133 7.5 1.56 294 101 175
1/25/2008 1195 7.06 704 77.6 35.5 132 7.1 1.55 332 102 183
2/27/2008 1221 6.60 690 77.8 35.4 133 7.5 1.56 335 95.9 174

Table 10--Chemical analyses of the monthly 2006-08 and other samples collected from Girard well 3.

Date
Sampled
Sp. Con.
(µS/cm)
pH TDS
(mg/L)
Ca
(mg/L)
Mg
(mg/L)
Na
(mg/L)
K
(mg/L)
Sr
(mg/L)
HCO3
(mg/L)
SO4
(mg/L)
Cl
(mg/L)
4/13/2006 1157 7.34 639 71.0 33.0 113 7.4 1.33 323 90.0 153
5/15/2006 1165 7.48 654 69.9 33.1 118 7.4 1.31 315 88.4 163
6/15/2006 1112 7.30 674 72.9 32.9 113 7.3 1.36 314 99.0 153
7/13/2006 1171 7.47 661 74.7 34.1 120 7.5 1.34 324 90.7 164
8/15/2006 1108 7.65 656 72.3 33.2 115 7.2 1.33 313 98.9 155
9/19/2006 1183 7.19 672 75.9 35.2 118 7.0 1.45 320 101 172
10/16/2006 1144 7.62 651 74.4 33.9 118 6.3 1.35 313 95.2 155
11/20/2006 1189 7.45 655 74.0 33.6 120 6.6 1.33 318 92.8 169
12/18/2006 1145 7.65 656 75.4 34.9 121 7.0 1.38 320 97.2 179
1/25/2007 1184 7.60 661 75.5 33.2 122 6.9 1.33 314 92.1 175
3/19/2007 1181 7.80 673 75.7 33.1 120 6.8 1.30 320 95.6 165
4/1/2007 1164 7.45 663 77.6 34.0 122 7.1 1.43 319 109 164
5/14/2007 1221 7.60 639 75.3 34.1 123 6.5 1.39 309 90.2 168
6/1/2007 1176 7.60 654 76.2 33.6 121 6.7 1.39 315 94.5 165
8/1/2007 1162 6.95 654 76.1 34.1 122 7.0 1.43 320 96.9 160
10/1/2007 1199 7.14 656 75.0 33.3 119 6.7 1.35 321 95.2 172
10/1/2007 1204 7.20 639 76.5 34.3 124 6.9 1.39 322 96.5 174
10/1/2007 1157 7.09 654 77.0 34.1 119 7.1 1.44 326 102 161
12/1/2007 1203 7.33 674 78.9 35.2 124 7.0 1.43 321 68.9 164
1/04/2008 991 7.30 661 76.4 34.0 120 7.0 1.40 319 99.3 159
1/25/2008 1116 7.28 656 74.9 33.7 117 6.8 1.40 321 101 160
2/27/2008 1164 6.97 672 76.1 33.7 123 7.0 1.39 321 94.7 161

Table 11--Chemical analyses of the monthly 2006-08 and other samples collected from Pittsburg well 8.

Date
Sampled
Sp. Con.
(µS/cm)
pH TDS
(mg/L)
Ca
(mg/L)
Mg
(mg/L)
Na
(mg/L)
K
(mg/L)
Sr
(mg/L)
HCO3
(mg/L)
SO4
(mg/L)
Cl
(mg/L)
4/13/2006 875 7.41 499 57.4 26.1 87.4 5.2 0.95 318 50.1 97.5
5/15/2006 911 7.43 517 61.4 27.9 90.7 6.6 0.97 315 56.1 107
6/15/2006 857 7.42 495 58.3 26.5 88.9 5.3 0.95 316 45.8 103
7/13/2006 897 7.47 509 59.1 26.9 88.8 6.1 0.95 322 47.0 111
8/15/2006 854 7.80 503 58.5 27.2 90.0 5.5 0.94 311 42.3 115
9/19/2006 913 7.75 516 59.2 27.0 88.9 4.6 0.95 319 57.9 109
11/20/2006 965 7.15 551 64.6 30.5 98.0 5.7 1.02 318 61.6 122
12/18/2006 907 7.75 514 59.3 27.5 90.3 5.0 0.95 319 46.4 117
1/25/2007 894 7.60 512 59.2 26.9 91.4 5.1 0.95 316 49.6 112
3/19/2007 900 7.60 515 59.7 26.5 89.1 5.2 0.90 319 55.2 110
3/20/2007 883 7.95 498 59.0 26.2 88.5 4.9 0.90 319 47.2 103
3/20/2007 882 7.80 506 58.6 26.0 87.7 5.0 0.90 318 54.4 106
4/1/2007 889 7.50 484 56.1 25.7 85.0 4.7 0.93 319 38.6 106
5/14/2007 904 7.60 494 58.7 26.2 88.1 4.9 0.96 315 42.6 107
10/1/2007 955 7.72 542 74.8 32.0 78.1 6.0 1.07 335 82.2 92.4
12/1/2007 991 7.24 535 65.6 29.9 92.6 5.2 1.01 319 49.2 125
12/1/2007 958 7.26 519 63.5 28.9 92.4 5.2 1.01 319 44.7 116
12/1/2007 933 7.31 510 62.0 28.4 91.3 5.1 0.99 320 42.9 112
12/1/2007 918 7.31 506 62.6 28.2 92.6 5.2 1.00 319 41.0 108
12/1/2007 903 7.35 498 61.1 27.6 91.6 5.3 0.99 320 38.9 104
1/25/2008 754 7.17 503 59.4 26.0 89.8 5.2 0.97 314 53.2 103
1/25/2008 858 7.31 500 58.7 26.0 88.5 4.9 0.96 319 48.0 106
2/27/2008 873 7.13 481 57.8 26.0 87.7 5.1 0.95 321 37.5 97.2
2/27/2008 874 7.17 495 57.9 26.3 88.3 5.2 0.96 323 45.3 101
2/27/2008 875 7.21 493 58.3 26.6 89.2 5.2 0.97 321 44.8 98.9
2/27/2008 875 7.13 506 58.8 26.7 89.9 5.2 0.98 322 53.2 102
2/27/2008 872 7.16 495 58.6 26.5 89.4 5.1 0.97 322 45.5 99.4
2/27/2008 875 7.18 502 60.2 27.3 91.8 5.3 1.00 322 45.5 102
2/27/2008 874 7.16 488 57.5 26.2 88.0 5.2 0.96 318 45.0 98.3
2/28/2008 869 7.16 495 58.7 26.5 89.7 5.3 0.98 320 45.7 100
2/28/2008 874 7.16 498 59.0 26.7 90.3 5.3 0.98 321 45.5 101
2/28/2008 873 7.20 494 58.2 26.4 88.9 5.2 0.97 322 45.4 99.5
2/28/2008 873 7.18 499 59.3 26.8 91.0 5.3 0.99 321 45.2 101

Table 12--Chemical analyses of the monthly 2006-07 samples collected from Pittsburg well 10. Water from this well was sampled when Pittsburg well 8 was unavailable.

Date
Sampled
Sp. Con.
(µS/cm)
pH TDS
(mg/L)
Ca
(mg/L)
Mg
(mg/L)
Na
(mg/L)
K
(mg/L)
Sr
(mg/L)
HCO3
(mg/L)
SO4
(mg/L)
Cl
(mg/L)
10/16/2006 873 7.23 516 59.2 27.0 88.9 4.6 0.95 319 57.9 109
6/1/2007 910 7.40 537 75.0 32.3 73.3 5.6 0.99 327 90.3 88.9
8/1/2007 934 6.96 545 75.2 32.4 78.4 6.0 1.07 333 86.3 90.8

Table 13--Chemical analyses of the monthly 2006-08 samples collected from the Weir city well.

Date
Sampled
Sp. Con.
(µS/cm)
pH TDS
(mg/L)
Ca
(mg/L)
Mg
(mg/L)
Na
(mg/L)
K
(mg/L)
Sr
(mg/L)
HCO3
(mg/L)
SO4
(mg/L)
Cl
(mg/L)
4/13/2006 707 7.54 423 62.1 29.7 47.8 5.69 1.04 325 61.3 35.0
5/15/2006 732 7.49 430 58.7 28.1 55.3 5.6 1.02 339 63.3 40.2
6/15/2006 722 7.55 440 61.1 29.5 61.4 5.4 1.07 344 59.9 40.7
7/13/2006 745 7.41 442 58.9 28.6 62.6 6.5 1.04 350 60.0 40.7
8/15/2006 700 7.85 417 60.5 29.4 51.0 5.8 1.04 327 61.0 36.5
9/19/2006 767 7.80 427 59.4 28.8 54.2 4.5 1.04 337 62.9 39.5
10/16/2006 824 7.34 497 49.5 27.2 97.0 4.2 1.10 405 53.0 55.0
11/21/2006 707 7.45 421 61.8 30.8 46.1 4.9 1.02 325 67.8 37.4
12/18/2006 726 7.65 432 59.6 29.9 56.6 5.1 1.03 339 62.2 39.0
1/26/2007 720 7.50 414 62.8 29.1 46.5 5.5 1.04 323 62.9 35.9
3/19/2007 720 7.80 424 61.7 28.8 48.1 5.2 1.00 329 68.7 36.7
4/1/2007 708 7.45 414 61.7 29.6 46.0 5.1 1.07 322 63.6 37.5
5/14/2007 723 7.50 414 63.7 29.3 47.0 5.2 1.07 319 62.6 37.0
6/1/2007 679 7.60 421 62.9 29.4 48.8 5.2 1.07 325 63.2 39.9
8/1/2007 701 7.21 421 63.0 29.4 48.3 5.3 1.07 334 62.9 35.2
10/1/2007 718 7.46 426 63.0 29.5 47.3 5.6 1.06 341 63.7 36.4
12/1/2007 744 7.36 396 61.7 29.1 46.5 5.3 1.05 327 45.0 35.5
1/25/2008 614 7.30 409 61.4 27.9 46.3 5.4 1.03 321 62.2 35.1

Table 14--Chemical analyses of samples collected during the June 2008 chemical-quality pumping test for Pittsburg 8.

Date/Time
Sampled
Sp. Con.
(µS/cm)
T
(°C)
pH TDS
(mg/L)
Ca
(mg/L)
Mg
(mg/L)
Na
(mg/L)
K
(mg/L)
Sr
(mg/L)
HCO3
(mg/L)
SO4
(mg/L)
Cl
(mg/L)
6/23/2008
11:01:00
968 22.5 6.89 566 70.9 32.1 100.8 5.8 1.10 315 68.8 131
6/23/2008
11:16:00
938 22.1 6.99 519 60.9 28.6 89.7 4.9 0.97 320 57.6 119
6/23/2008
11:31:00
935 22.1 6.93 521 62.7 29.2 92.2 5.1 1.00 318 56.6 118
6/23/2008
11:46:00
931 22.1 6.99 505 60.5 28.3 89.4 5.0 0.97 312 53.4 113
6/23/2008
12:14:00
922 22.4 6.97 519 61.2 28.8 90.7 5.0 0.98 319 55.1 119
6/23/2008
13:21:00
917 23.0 6.95 522 61.1 28.9 91.0 5.1 0.99 320 58.3 118
6/23/2008
14:21:00
919 22.8 6.94 523 61.2 28.8 91.7 5.1 1.00 318 60.9 117
6/23/2008
15:21:00
914 22.8 6.96 500 59.6 26.6 88.8 5.0 0.95 319 50.9 110
6/23/2008
16:29:00
906 22.8 7.04 506 59.4 28.6 89.8 4.9 0.98 317 50.9 115
6/23/2008
17:29:00
902 22.8 7.05 499 61.5 27.8 91.3 5.0 0.98 318 52.8 103
6/23/2008
18:29:00
894 22.6 7.10 515 61.4 27.4 91.4 5.2 0.99 319 58.5 113
6/23/2008
20:29:00
896 22.2 7.00 494 59.4 27.0 88.8 5.1 0.96 320 52.3 103
6/23/2008
22:29:00
888 21.7 7.01 493 59.3 26.9 88.9 5.1 0.97 320 47.2 107
6/24/2008
7:19:00
878 20.7 7.02 494 59.0 27.0 89.5 5.1 0.97 321 51.4 103
6/24/2008
9:19:00
874 21.4 6.99 477 56.1 25.8 85.6 4.9 0.92 321 41.5 104
6/24/2008
11:19:00
873 22.1 7.07 486 57.8 26.4 88.0 5.0 0.95 321 43.9 105
6/24/2008
13:19:00
876 22.6 7.05 485 58.1 26.6 88.9 5.0 0.96 319 47.7 100
6/24/2008
15:19:00
876 22.2 6.89 475 57.3 26.1 87.7 4.9 0.95 320 41.5 99
6/24/2008
17:19:00
872 22.3 6.99 450 58.0 26.4 88.3 5.0 0.96 323 41.6 99.9
6/24/2008
19:19:00
871 21.9 6.93 490 58.3 26.6 88.8 5.1 0.97 319 50.6 103
6/24/2008
21:19:00
869 21.8 6.99 475 57.1 26.0 87.3 5.0 0.95 320 43.8 97.1
6/24/2008
23:19:00
863 21.8 6.97 480 58.7 26.6 89.6 5.1 0.98 319 39.9 102
6/25/2008
7:28:00
866 21.1 6.95 458 56.2 25.8 86.3 5.0 0.93 320 35.6 89.9
6/25/2008
9:28:00
865 21.5 6.94 457 56.5 25.8 86.8 5.0 0.94 322 35.3 88.2
6/25/2008
11:28:00
865 22.3 6.96 470 58.1 26.3 88.5 5.1 0.96 315 39.8 95.6
6/25/2008
13:28:00
871 22.4 7.04 478 57.6 26.3 88.4 5.0 0.96 322 40.2 101

Table 15--Chemical analyses of samples collected during the September 2008 chemical-quality pumping test for Pittsburg 8.

Date/Time
Sampled
Sp. Con.
(µS/cm)
T
(°C)
pH TDS
(mg/L)
Ca
(mg/L)
Mg
(mg/L)
Na
(mg/L)
K
(mg/L)
Sr
(mg/L)
HCO3
(mg/L)
SO4
(mg/L)
Cl
(mg/L)
9/2/2008
9:40:00
975 22.0 7.2 520 64.7 29.2 94.0 5.3 1.04 315 53.9 116
9/2/2008
10:10:00
974 21.9 7.11 543 64.4 29.1 94.0 5.2 1.04 316 62.2 131
9/2/2008
10:40:00
972 22.0 7.32 533 65.5 28.6 93.0 5.3 1.01 316 60.4 123
9/2/2008
11:10:00
969 22.8 7.26 529 65.0 28.7 92.0 5.2 1.00 320 47.6 132
9/2/2008
11:40:00
970 23.3 7.17 524 63.6 28.5 90.0 5.1 0.98 317 65.7 114
9/2/2008
12:10:00
968 23.8 7.11 509 64.3 28.8 91.0 5.2 0.99 317 51.3 111
9/2/2008
12:40:00
928 23.6 7.09 505 62.0 27.7 89.0 5.0 0.96 317 51.2 113
9/2/2008
13:40:00
933 23.4 7.15 517 65.0 29.5 93.0 5.2 1.01 317 48.5 118
9/2/2008
14:40:00
961 23.5 7.17 507 63.5 29.0 92.0 5.2 0.99 318 49.0 110
9/2/2008
15:40:00
931 23.3 7.02 487 61.7 28.4 91.0 5.3 0.94 317 46.3 97
9/2/2008
16:40:00
956 23.3 7.11 514 64.0 29.2 92.0 5.1 1.01 318 58.6 107
9/2/2008
17:40:00
953 23.0 7.15 505 61.9 28.5 90.0 5.0 0.98 317 51.9 110
9/2/2008
18:40:00
950 22.4 7.18 485 60.6 28.1 90.0 5.3 0.92 317 46.0 98
9/2/2008
20:40:00
927 21.3 7.13 494 63.0 28.5 92.0 5.1 1.00 317 45.3 103
9/2/2008
22:40:00
945 21.3 7.14 516 63.8 28.9 94.0 5.2 1.02 317 54.3 112
9/3/2008
1:40:00
937 7.18 503 62.7 28.5 92.0 5.1 1.00 317 52.9 104
9/3/2008
4:40:00
928 7.24 506 63.1 28.3 93.0 5.2 1.01 316 50.8 109
9/3/2008
7:40:00
916 19.4 7.21 513 63.3 28.7 93.0 5.1 1.02 318 57.6 107
9/3/2008
10:40:00
926 20.6 7.27 503 61.1 27.5 90.0 5.0 0.99 318 49.6 112
9/3/2008
13:40:00
928 20.6 7.28 501 62.3 28.4 92.0 5.3 1.00 318 53.6 102
9/3/2008
16:40:00
918 20.3 7.27 503 61.9 27.6 92.0 5.1 1.00 317 50.3 109
9/3/2008
19:40:00
919 20.2 7.30 496 60.9 27.5 92.0 5.4 0.99 318 46.1 106
9/3/2008
22:40:00
913 20.1 7.29 493 61.3 27.2 91.0 5.1 0.99 318 45.1 105
9/4/2008
1:40:00
910 7.33 506 61.5 27.5 92.0 5.1 1.00 317 46.9 116
9/4/2008
4:40:00
913 7.34 487 58.8 26.2 88.0 4.9 0.95 317 44.0 108
9/4/2008
7:40:00
908 20.3 7.34 489 60.0 27.0 90.0 5.0 0.98 318 42.6 106
9/4/2008
10:40:00
910 20.1 7.28 484 59.6 26.8 89.0 5.0 0.97 316 42.0 105
9/4/2008
12:57:00
907 21.6 7.32 500 62.6 27.8 93.9 5.1 1.02 317 52.1 102

Graphical displays of the concentration data were used to explore spatial and temporal relationships and develop mixing relationships between constituents and constituent ratios that represent the contributions of end-member ground waters of differing chemistry to the produced waters sampled in this project. The diamond-shaped field of the Piper diagram (Piper, 1944) was modified by rotation of the coordinate axes 90° to allow for easier plotting and display of the monthly sample data from spreadsheets.

Mixing curves are useful for testing the hypothesis that a given water is a mixture of two end-member waters of differing chemistry based on their dissolved constituents. In the case of two end-member mixtures, the relationship between relative amounts and observed end-member concentrations and the mix in a water sample can be expressed as a mass balance equation (Hem, 1985):

C1V1 + C2V2 = C3(V1 + V2),     (1)

where C1 and C2, and V1 and V2, are the constituent concentrations and the volumes from sources 1 and 2, respectively, and C3 and (V1 + V2) are the constituent concentration and the volume of water produced at the well. In the case of relative contributions, the quantity (V1 + V2) is equal to 1, and V1 and V2 are volume fractions.

Monthly pumpage data could not be obtained for most of the wells sampled because of the manner in which water withdrawals are tabulated by the water utilities. Some of the utilities rely on sources of both ground water from the Ozark Plateau aquifer system and surface water from Bone Creek Reservoir in Crawford County. Thus, it is difficult to quantify withdrawals from individual wells. However, on the basis of the types of pumps, the pumping rate, and frequency of use information, it is likely that Pittsburg 8 and Girard 3 are used more heavily than any of the other wells in this study.


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