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<br />COLORADO DEPARTMENT OF HEALTH, Water Quality Control Division <br />Rationale, Page 3 Permit No. CO-0026981 <br />AMENDMENT NO 1 (Continued): <br />arsenic (0.05 mg/1), chromium (0.1 mg/1 - trivalent, sad 0.025 mg/1 - <br />hexavalent), iron, (total, 1.0 mg/1), manganese, (total, 1.0 mg/1), nickel <br />(0.05 mg/1), selenium (0.02 mg/1), dissolved oxygen (6.0/7.0 mg/1), pH (6.5 - <br />9.0 s.u.), fecal coliform bacteria (2000 per 100 ml), ammonia (unionized, 0.02 <br />mgfl), residual chlorine (0.003 mg/1), cyanide (free, 0.005 mg/1), sulfide <br />(undissociated, 0.002 mg/1 as S), boron (D.75 mg/1), and nitrite (0.05 mg/1). <br />In determining the changes in this permit's effluent limitations for cadmium, <br />copper, lead, mercury, and zinc, two other revisions were also made during the <br />time of the water quality standards redeterminations. New seasonal design <br />(Q7-10) low flows for the Canyon Creek above the Camp Bird Mine discharge <br />were determined. The effluent flow which is projected to occur for each <br />season under Q7_10 low flow stream conditions was also determined. These <br />two flow values for each season are summarized below. <br />Table 2: Canyon Creek Low Flows and Facility Flows <br />Season: Nov. - April May - July Aug. - October <br />Stream Q7-10 Low Flow, cfs 2.7 6.3 3.9 <br />Discharge Design Flow, cfs 1.5 1.3 3.5 <br />The revised Q7-10 seasonal low flows for Canyon Creek, which are based upon <br />the use of gauging station data for the Uncompahgre River near Ridgeway and <br />also the watershed area ratios for the Canyon Creek area above the discharge <br />and for the area including the Uncompahgre River at the gaging station, were <br />determined by the Division and a consultant far Chipeta Mining Corp. <br />Since the facility discharge design flow and the Q7_lD stream low flow were <br />determined and agreed upon previously by the Division and the permittee, the <br />new design stream Low flows (chronic Q3E30 flow for determining 30-day <br />average limitations, and acute Q1E3 flow for determining the daily maximum <br />limitations) were not used for this amendment. However, these new design <br />stream low flows will be used to evaluate limitations for the next renewal <br />permit. <br />The facility discharge design flow represents an estimate of the facility flow <br />which would occur under stream Q7_10 low flow conditions. This relationship <br />is based upon a correlation that was found between facility discharge flows <br />and the downstream flows. According to a consultant's report for the <br />permittee (referenced following in the ambient data discussion), "the volume <br />of flow discharged from the mine is directly related to the snow pack with the <br />peak discharge of the mine lagging peak flows in the stream by about two <br />months. Because of this phenomena, peak discharges will never occur during <br />minimum stream flows and will always occur on the descending curve of the <br />hydrograph. In addition, the mine discharge will be directly related to the <br />amount of snow pack and precipitation in the basin which also established the <br />flow in Canyon Creek." <br />