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8.0 GROUND -WATER QUALITY <br />8.1 Major Ions and Dissolved Solids <br />Ground -Water Quality Deteriorates from West to East <br />Across Area 61 <br />The water quality deteriorates as water flows from sandstone, conglomerate, and <br />basalt in plateaus and mesas to shale in stream valleys and plains. <br />From west to east across the area, concentrations <br />of dissolved solids increase and the ground water <br />changes from bicarbonate to sulfate and chloride in <br />composition (figs. 8.1 -1 and 8.1 -2). The regional <br />chemical evolution of ground water is summarized in <br />figure 8.1 -3. <br />Area 61 is higher on the western side than on the <br />eastern side (fig. 8.1 -2), and as ground water flows <br />down this topographic gradient, it gains dissolved <br />solids by reaction with bedrock. Geologic forma- <br />tions on the western side of the area are predomi- <br />nantly sandstone and conglomerate, which consist of <br />minerals, such as quartz, that resist reaction with <br />ground water. Precipitation and surface water that <br />infiltrate these rocks and become ground water are <br />calcium bicarbonate solutions containing few dis- <br />solved solids. Because sandstone and conglomerate <br />minerals do not react readily with ground water, the <br />ground water is little changed as it flows through the <br />rock. Geologic formations on the eastern side of the <br />area are predominantly shale, which is composed of <br />clay minerals and salts that react readily with ground <br />water. Ground water flowing through shale thus <br />becomes very mineralized. In the central part of the <br />area, geologic formations consist of nearly equal <br />quantities of sandstone and shale, and ground water <br />there is intermediate in composition and quality <br />between ground waters on the western and eastern <br />sides of the area. <br />Regional trends in ground -water quality are dis- <br />rupted by topographic and geologic features. As <br />ground water flows from stream divides to stream <br />valleys, it gains dissolved solids (fig. 8.1 -2). Human <br />activities, such as mining or irrigated agriculture, <br />also add dissolved solids to ground water in valleys. <br />Ground water in valleys with intermittent or ephe- <br />meral streams is thus more mineralized than in <br />stream- divide areas. In valleys with perennial <br />streams, the streamflow may be sufficient to flush <br />out dissolved minerals and cause water in alluvium <br />and shallow bedrock to be less mineralized than in <br />adjacent bedrock. Ground water in volcanic- capped <br />mesas contains few dissolved solids because the vol- <br />canic rocks are very permeable and rapidly transmit <br />water. The origin of highly mineralized sodium <br />chloride ground water near the Spanish Peaks, an <br />intrusive stock, and related dikes is obscure, but the <br />composition of the ground water may result from <br />reactions with gases emanating from the igneous <br />rocks. <br />72 <br />Geologic formations are distinguishable by their <br />ground -water quality. The Devils Hole - Farasita, Cu- <br />chara Poison Canyon, and volcanic rock aquifers <br />contain mostly calcium bicarbonate water with less <br />than 500 milligrams per liter of dissolved solids. The <br />Huerfano Formation contains mostly calcium sulfate <br />water with 500 to 1,500 milligrams per liter of dis- <br />solved solids. The Raton - Vermejo- Trinidad aquifer <br />contains mostly sodium bicarbonate water with 500 <br />to 1,500 milligrams per liter of dissolved solids. <br />Cretaceous shale, limestone, and sandstone contain <br />mostly sodium sulfate, calcium sulfate, and sodium <br />chloride water with 1,000 to more than 5,000 milli- <br />grams per liter of dissolved solids. Within each <br />formation, water generally is least mineralized in <br />topographically high areas and more mineralized in <br />topographically low areas. <br />Sources of ground -water quality data include <br />Griggs (1948, p. 159 -176), Powell (1952, p. 30), <br />McLaughlin and others (1961, p. 17 -18), Dinwiddie <br />(1964, p. 15), Hart and Smith (1979, p. 50 -51), <br />Water, Waste, and Land, Ltd. (1980, appendix E), <br />Repplier and others (1981, pl. 5), Howard (1982, <br />appendix K), Kaiser Steel Corp. (written commun., <br />1981), and unpublished U.S. Geological Survey data. <br />