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<br /> <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br /> <br />11-5 <br /> <br />Two aquatic species of special interest occur in the area. A popu- <br />lation of greenback cutthroat trout, a Federally endangered species, is known <br />to occur in Como Creek, a tributary to North Boulder Creek. The johnny <br />darter, which occurs in the foothi lis zone of St. Vrain Creek, is currently <br />I isted as a threatened species in Colorado by the Colorado Division of Wi Id- <br />life. <br /> <br />3. Water Quality <br /> <br />Water quality in the St. Vrain Creek Basin is highly variable. The <br />headwaters and upstream reaches have good to excellent water quality while <br />there is significant deterioration in several water qual ity parameters down- <br />stream from Lyons. The upper reach, above the town of Lyons, is characterized <br />by generally good water quality with low water temperature, high dissolved <br />oxygen and rocky and gravel bottoms. This upper segment of the Basin general- <br />ly maintains sustained flows. <br /> <br />A 1983 study of St. Vrain Creek indicated that the water quality of <br />the stream at Lyons is good and meets the state stream standards of a Class I <br />cold water fishery. Water qual ity below Lyons to Hygiene Road also appears to <br />be capable of supporting a Class I cold water fishery; however, periods of low <br />stream flow during the winter months appear to be the limiting factor in sus- <br />taining a fishery (DRCOG, 1983c). <br /> <br />The St. Vrain streambed through the Lyons and Longmont reaches is <br />si Ited as a result of increased development along stream banks and the resul- <br />tant increases in storm runoff. Agricultural withdrawals below Lyons have <br />reduced flows considerably from those of the past. Water qual ity downstream <br />of Longmont is generally poor due to agricultural return flows. <br /> <br />Non-point sources deliver significant quantities of pollutants to <br />the St. Vrain Basin waterways; however, few data are avai lable for quantifying <br />the relative contribution of non-point to point source pollution. The data <br />indicate that loadin9 from non-point sources for total dissolved sol ids, fecal <br />coliforms, fecal streptococci, and nitrates outweigh loadings from point <br />sources. Ammonia and phosphate contributions from point sources exceed those <br />from non-point sources. Significant loadings of organic materials (BOD) occur <br />from both point and non-point sources. It is believed that agricultural irri- <br />gation return flows are the primary cause of the high total dissolved solids <br />contributions from non-point sources. The high levels of microorganisms <br />del ivered to St. Vrain streams are bel ieved to be a resul t of stormwater <br />runoff (DRCOG, 1981). <br /> <br />Water qual ity data from the EPA STORET retrieval system were analy- <br />zed for five sampling stations in the upper and lower basins. Data summaries <br />are shown in Table 11-1. Measured pH levels increase as the St. Vrain Creek <br />flows from the high mountain sources through the foothi lis down through the <br />plains to Weld County. The increase in pH provides evidence of dissolved salt <br />loading which buffers the water at higher pH levels. This is supported by <br />data which show significant increases in conductivity from 28 to 1,300 mg/l as <br />