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COLORADO <br />+y��_ ,�� Water Quality Assessment <br />„:9 <br />Department of Public <br />Health b Environment <br />The ratio of the low flow of No -Name Gulch, East Pyeatt Gulch, Middle Flume Gulch, East Middle Flume <br />Gulch, East Flume Gulch, Oak Gulch and Deacon Gulch to the Trapper Mine facility design flow is 0:1.Note <br />that for streams with a low flow of zero, the ambient water quality discussion is unnecessary. <br />To determine the low flows of the Yampa River near the Trapper Mine facility, USGS 09247600 (Yampa River <br />below Craig) located on the Yampa River immediately downstream from the confluence with Johnson Gulch <br />was used. This gage is the nearest gage that provides a recent period of record. Daily flows from the gage <br />station were obtained for a period of record from January 2005 through September 2016, and the annual 1E3 <br />and 30E3 low flows were calculated using US EPA DFLOW software. The output from DFLOW provides <br />calculated acute and chronic low flows for each month and are presented in Table A -6b. This is a downstream <br />gage. Based on the facility DMR for the previous permit term, the outfalls have not discharged at design flow <br />and discharge sporadically. Therefore, it was determined that the facility flow has a negligible effect on the <br />statistics used to calculate low flows. Further, this section of the Yampa river is a Threatened and <br />Endangered Species receiving water, and therefore no dilution is allocated for all aquatic life parameters. <br />Therefore, it was not necessary to subtract the facility flow from the daily flows obtained at this gage station. <br />Table A -6b <br />Table A -6a <br />Low Flows <br />for No -Name Gulch, East Pyeatt Gulch, Middle Flume Gulch, East Middle Flume Gulch, <br />East Flume Gulch, Oak Gulch and Deacon Gulch at the Trapper Mine <br />7E3 <br />0 <br />0 <br />0 <br />0 <br />0 <br />0 <br />0 <br />0 <br />0 <br />0 <br />0 <br />0 <br />0 <br />Chronic <br />Apr <br />May <br />Jun <br />Jul <br />Aug <br />Sep <br />Oct <br />Nov <br />Dec <br />(cfs) <br />30E3 <br />0 <br />0 <br />0 <br />0 <br />0 <br />0 <br />0 <br />0 <br />0 <br />0 <br />0 <br />0 <br />0 <br />Chronic <br />174 <br />296 <br />78 <br />99 <br />73 <br />70 <br />73 <br />98 <br />70 <br />Acute <br />The ratio of the low flow of No -Name Gulch, East Pyeatt Gulch, Middle Flume Gulch, East Middle Flume <br />Gulch, East Flume Gulch, Oak Gulch and Deacon Gulch to the Trapper Mine facility design flow is 0:1.Note <br />that for streams with a low flow of zero, the ambient water quality discussion is unnecessary. <br />To determine the low flows of the Yampa River near the Trapper Mine facility, USGS 09247600 (Yampa River <br />below Craig) located on the Yampa River immediately downstream from the confluence with Johnson Gulch <br />was used. This gage is the nearest gage that provides a recent period of record. Daily flows from the gage <br />station were obtained for a period of record from January 2005 through September 2016, and the annual 1E3 <br />and 30E3 low flows were calculated using US EPA DFLOW software. The output from DFLOW provides <br />calculated acute and chronic low flows for each month and are presented in Table A -6b. This is a downstream <br />gage. Based on the facility DMR for the previous permit term, the outfalls have not discharged at design flow <br />and discharge sporadically. Therefore, it was determined that the facility flow has a negligible effect on the <br />statistics used to calculate low flows. Further, this section of the Yampa river is a Threatened and <br />Endangered Species receiving water, and therefore no dilution is allocated for all aquatic life parameters. <br />Therefore, it was not necessary to subtract the facility flow from the daily flows obtained at this gage station. <br />Table A -6b <br />Low Flows for the Yampa River near the Trapper Mine <br />Low <br />Flow <br />Annual <br />Jan <br />Feb <br />Mar <br />Apr <br />May <br />Jun <br />Jul <br />Aug <br />Sep <br />Oct <br />Nov <br />Dec <br />(cfs) <br />1E3 <br />70 <br />90 <br />95 <br />123 <br />174 <br />296 <br />78 <br />99 <br />73 <br />70 <br />73 <br />98 <br />70 <br />Acute <br />7E3 <br />84 <br />108 <br />110 <br />123 <br />174 <br />296 <br />93 <br />93 <br />84 <br />84 <br />85 <br />111 <br />96 <br />Chronic <br />30E3 <br />113 <br />119 <br />120 <br />123 <br />174 <br />296 <br />140 <br />113 <br />113 <br />113 <br />113 <br />115 <br />115 <br />Chronic <br />During the months of March, April and May, the acute low flow calculated by DFLOW exceeded the chronic <br />low flow. In accordance with Division standard procedures, the acute low flow was thus set equal to the <br />chronic low flow for these months. <br />Mixing Zones <br />The amount of the available assimilative capacity (dilution) that may be used by the permittee for the <br />purposes of calculating the WQBELs may be limited in a permitting action based upon a mixing zone analysis <br />or other factor. These other factors that may reduce the amount of assimilative capacity available in a <br />permit are: presence of other dischargers in the vicinity; the presence of a water diversion downstream of <br />the discharge (in the mixing zone); the need to provide a zone of passage for aquatic life; the likelihood of <br />bioaccumulation of toxins in fish or wildlife; habitat considerations such as fish spawning or nursery areas; <br />the presence of threatened and endangered species; potential for human exposure through drinking water <br />or recreation; the possibility that aquatic life will be attracted to the effluent plume; the potential for <br />adverse effects on groundwater; and the toxicity or persistence of the substance discharged. <br />PagQe 17 of 40 � <br />4300 Cherry Creek Drive S., Denver, CO 80246-1530 p 303-692-2000 www.cotorado.gov/cdphe/wqcd I \ / <br />