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MgCa-HC03504 type (1980), 523 and 541 waters are characterized as a t1g-504 water type. • <br />Site 545 (Dry Creek drainage) is also characterized as a Mg-504 water type. <br />Schoeller diagrams of Sites 51, 55, 57, 523, 541, and S45 are shown in Appendix 7-7. The <br />diagrams plot ion chemistry in units of mi lliequivalents per liter (meq/1). Overall, the <br />diagrams show parallel trends for 51, 523, and :i45, indicating little seasonal variability <br />and consistent water chemistry for the time periods represented by the samples. The lack <br />of complete, quarterly, geochemical data from springs in the drainages precludes any <br />quantitative interpretation of year-round seasonal trends. <br />The Schoeller diagram of 57 indicates there was considerable variation of Mg, C7, and 50 <br /> 4 <br />between the time periods represented by the seven samples. The diagram for 541 shows a <br />trend similar to 57. For Sites S7 and 541, Mg and 50 <br />correspond with an increase in TDS, <br /> 4 <br />whereas, C1 corresponds with a decrease in TDS. This information suggests that when <br />seasonal evapotranspiration rates are high or the amount of seasonal recharge is lower, <br />the TDS content of the spring water increases, particularly Mg and 50 <br />concentrations. <br /> 4 <br />When evaporation rates are lower and/or the amount of annual recharge is greater, the TDS <br />of the water is lower and so are the concentrations of Mg and 504. Generally, the TD5 • <br />content of spring water increases from the late spring to early fall when ambient air <br />temperatures are highest. <br />The water chemistry of 525 was first noted in July, 1979 as unique because of its high <br />concentration of dissolved solids. Several ideas were offered to explain the water <br />chemistry at this site, but it appears that the water quality is natural and <br />lithologically controlled. Evapotranspiration may contribute at a small level to the high <br />solids content of the water at 525. Such a high TDS concentration (26,566 mg/1 average) <br />in water at 525 categorizes it as saline water since the TDS level exceeds 10,000 mg/1. <br />This spring has high fluoride and nitrate concentrations, which are probably due to <br />natural conditions as well. Spring Site 523 is also quite high in dissolved solids. <br />Suitability. Spring water suitability at Seneca II-W was evaluated by comparison of <br />sample analyte concentrations to the most stringent standards established by State and <br />Federal agencies based on categories of ultimate use. State agencies, Colorado Department <br />of Health (CDOH) and Colorado Mined Land Reclamation Division (CMLRD), and Federal <br />agencies, U.S. Environmental Protection Agency (EPA) and the Office of Surface Mining • <br />Reclamation and Enforcement (OSMRE), have established limits for analyte concentrations in <br />72 <br />