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• Ground Water Suitability. The constituent concentrations for wells HGDALI, HGDAL2, and HGDAL3 <br />presented in Table 7-1 through 7-3 ware compared against agriculture water quality ar°^~+-~+° <br />. promulgated by the Colorado Department of Public Health and Environment (CDPHE) to assess the <br />suitability o£ the water for agricultural uses. In addition to the CDPHE sr°^.+=..+°, select <br />constituents (TDS and SOS) xarg cou~ared against Wyoming Division of Environmental Quality <br />(YIDEQ) standards as reference guidelines for specific agricultural uses. The WDEQ standards, <br />while not promulgated in Colorado, era widely used within the industry ss use-suitability <br />guidelines. The WDEQ sta^.d~^'+° are o£ interest because they set guidelines for two separate <br />agricultural uses; one list o£ s*a^'+~+++~ (or guidelines) for irrigation use and a second (lase <br />atrinyent) lint o£ standards (guidelines) for livestock use. In contrast, CDPHE's ground <br />water agricultural sr°^~+=+•+° are generally for irrigation of crops. <br />Ground water trace metal cancantrations prior to 1993 were reported as the total metals <br />fraction. The CDPE9: atar~~^'+° are for the dissolved concentration. Consequently, trace metal <br />values prior to 1993 era not directly comparable to the CDPHE atandar+d. <br />Well HGDALI chemistry, in comparison to CDPHE's agriculture s*°^'+°~"+°, exoaedad the B limit Of <br />0.75 mq/1 three times between 1993 and 1995, the Mkt limit of 0.2 mq/1 four times between 1993 <br />and 1995, and the 9e limit o£ 0.02 mq/1 once. 3averal constituents including H, Cd, t4i, and <br />Pb had total concentrations in samples collected prior to 1993 which were greater than the <br />CDPHE sr°^'+°^+, but a comparison between the atar~=+~'+ and the measured value may not be <br />appropriate. CDPHE classifies ground water as "Agriculture Oae-Quality^ when the background <br />. TDS value is lase than 10,000 mg/1. Well H®AL1 exceeded the CDPFIE TDS value of 10,000 for <br />all 19 sampling events. FIDEQ guidelines for TDS era 5000 mg/1 and 2000 mg/1 for livestock <br />watering and irrigation, respectively, while the SO. guideline oP 3000 mg/1 is for liveetorJr <br />watering. Well HGDAi.l TDS and 30. concentrations also exceeded the WDEQ guidelines for all 19 <br />sampling events. The comparison between CDPHE agricultural atan~:_^'+~ and WDEQ guidelines and <br />concentrations reported in H®AL1 samples indicates that the water in well HGDALI is not <br />suitable £or use ae either livestock drinking water or irrigation water. The major <br />constituents rendering the water unsuitable era H, bfi, SO., and TDS. In addition, SAR levels <br />ranged from 30-59 rhirh results in the rater receiving a "poor classification" rating for <br />irrigation use, with the water posing an extm®e sodium hazard for the soil. <br />Well HGDAL2 rhPmiatry, in coa~arison to CDPEO:'s agriculture standards exceeded the B limit of <br />0.75 mg/1 and the [M limit of 0.2 mg/1 for nll five sampling events batmen 1993 and 1995. <br />Several constituents including H, Cd, tM, and Pb had total concentrations in samples collected <br />prior to 1993 which wawa greater than the CDPHE ar°^.+..,~, but a comparison between the <br />standard and the measured value may not be appropriate. Wall HCAAL2 exceeded the CDPHE TDS <br />value of 10,000 mg/1 for all 17 sampling events. Zn addition, the TDS and SO. conc>3ntr4tions <br />exceeded the WDEQ guidelines for all 17 sampling events. The comparison between COPFO: <br />agricultural atarLa ~+•+° and FIDEQ guidelines and mncentrationa reported in H((~~AI.2 samples <br />indicates that the water in roll HGDALl is not suitable for use as either livestock drinking <br />water or irrigation rater. Tha major conatituanta *+°^'+°^ing the water unsuitable are H, FIIt, <br />SO, and TDS. In addition, SAR levels ranged from 7-27 which results in the rater receiving a <br />"fair classification" rating for irrigation use, rich the water posing a sodium hazard £or the <br />soil. <br />• <br />RN-o~ <br />13 Revised 2/9B <br />