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• Tables 39, 40, and 41 provide summaries of the 1999 Water Year data collected a[ each site. Tables 39a, 40a, and <br />41a provide period of record statistical summaries of collected data at each site. Figures 74 through 81 and 118 <br />through 121 provide graphical representations of water levels and selected water quality parameters recorded at <br />each site. Typical Flow panerns were exhibited at these sites vvi[It spring runoff periods accounting for the peak <br />flows observed. At all of these sites, the inverse relationship between Flow and field conductivity continues to be <br />evident. <br />1999 Water quality parameters for these sites are typically within previously established ranges with a few <br />exceptions. A[ site 8 (Table 40) new maximum values were recorded for lab pH and alkalinity. At site 900 <br />(Table 41) a new maximum value was recorded for SAR. <br />Fish Creek: Five surface Flow monitoring sites on Fish Creek are utilized. Site 16 is located upstream of [he <br />Mine 2 area; site 302 is located downstream of the Fish Creel Borehole mine dewatering site; site 1002 is located <br />approximately 2 miles further downstream and is monitored in conjunction with alluvial well 006-AW-2; site <br />27A is located near the Fish Creek Tipple; and site 1003 is located downstream of the Fish Creek Tipple. During <br />1999, the Fish Creek surface water monitoring sites generally required monthly flow and field parameter <br />measurements with quarterly water quality sample collection. The monitoring requirements for all sites except <br />302 are further described to require 12 flow and field parameter monitoring instances [o occur between Marctt <br />and September along with 4 water quality sampling events. All monitoring requirements were fulfilled at these <br />sites in 1999. Required monitoring at site 302 included monthh~ flow, field parameter, and water quality <br />• sampling during [he irrigation season June through September. Site visitation requirements were met at site 302 <br />Tables 44 through 48 provide summaries of the 1999 Water Year data collected at Fish Creek surface Flow sites. <br />Tables 44a through 48a provide period of record statistical summaries of collected data at each site. Figures 82 <br />through 101 provide graphical representations of water levels and selected water quality parameters recorded at <br />each site. Again, typical flow patterns were exhibited at these sites with spring runoff periods accounting for the <br />peak flows observed. Runoff magnitudes were in some instances derived from the extreme high end of the rating <br />curves developed for each site. These values represent best estimates but are unsubstantiated with measured data. <br />At all sites, the inverse relationship between Flow and field conductivity was evident. <br />1999 Water quality parameters for these sites are q~pically within previously established ranges with a few <br />exceptions. At site 16 (Table 44) a new minimum value was recorded for lab pH. At site 302 (Table 45) a new <br />minimum value was recorded for bicarbonate; and neva maximum values were recorded for molybdenum and <br />anttnia-free nitrogen. At site 1002 (Table 46) a new minimum value was recorded for lab pH; and new maxitnttnt <br />values were recorded for bicarbonate and amnia-free nitrogen. At site 1003 (Table 48) a new maximum value <br />was recorded for alkalinity. <br />Trout Creek: Tlvee surface flow monitoring sites on Trout Creek are utilized. Site 301 is located on Trout Creek <br />above the confluence with Middle Creek: site 69 is located on Trout Creek below the conFluence; and site 100, <br />• established in 1994, is located downstream of conFluence of Fish Creek and Trout Creek. Required monitoring <br />for these sites included monthly flow, field parameter, and water quality sampling during the irrigation season <br />_g <br />