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• parameters. If a spring is discharging 35 gallons per minute or greater, it is monitored <br />throughout the remainder of the year in accordance with the monitoring plan. <br />The field data for the 1997 spoil spring monitoring program is presented on Table 30. A plot of <br />the historic flow data for Pond 87 and spoil spring 114 is presented on Figure 64. Due to <br />pumping of Site 114 for water supply by Twentymile Coal Company, discharge from the spring <br />occurred for only a short period during the spring. The associated discharge from Pond F <br />ceased by mid-June. Short term discharges were also recorded in August and September. <br />None of the spoil springs at Mine 2 exceeded the 35 gpm threshold in June 1997. A full suite <br />sample was collected as required however from the O-Comp site as this represented largest <br />spoil spring occurring at Mine 2. Eight additional springs with flows greater than 35 gpm were <br />recorded at Mine 1 and Eckman Park. Spring D Comp serves as a composite sampling point <br />for the A, B, and C series springs at Eckman Park above Pond A. The flow data indicates that <br />the spoil springs follow the same pattern as the surface runoff: very low flow during most of the <br />year and a very rapid increase in flow during the spring runoff followed by a moderately rapid <br />decrease in flow. <br />1997 water quality data for spoil springs which were sampled for water quality are presented <br />on Tables 31 through 43. Tables 31a through 43a provide period of record statistical <br />summaries for the monitored sites and Tables 31b through 43b provide period of record flow <br />summaries for the sites. <br />The data for the Mine 1 spoil springs shows a maximum field conductivity value of 3910 <br />umhos/cm (Spring 1891603) with a flow weighted average value of approximately 3064 <br />umhos/cm during the 1997 water year. Spring 114 is typically the dominant influence in this <br />area during the Annual Spring Survey. However, at the time of the survey this spring was <br />being utilized for the mine water supply. The data for the Mine 2 spoil springs show a <br />maximum field conductivity value of 31300 umhos/cm with a flow weighted average value of <br />approximately 1550 umhoslcm during the 1997 water year. The data for the Eckman Park <br />spoil springs show a maximum field conductivity value of 4250 umhos/cm (OV61TD) with a <br />flow weighted average value of approximately 3765 umhos/cm during the 1997 water year. <br />During the winter when Foidel Creek flows are dominated by spoil spring discharges, the <br />creek's conductivity level approaches that of the spoil springs. The conductivity of the spoil <br />springs shows temporal fluctuations that most likely reflect spoil recharge events of low TDS <br />snowmelt. The lowest TDS concentrations in the spoil springs typically occur during the Spring <br />snowmelt period. <br />Figure 70 indicates that the water quality in Foidel Creek (Site 8) is influenced by the water <br />quality of the discharge from Pond A. Pond A receives the discharge of the largest spoil <br />springs. The spoil spring 114 discharge, which feeds site 87 (Pond F) is characterized by high <br />dissolved solids, calcium, magnesium, sulfate and SAR compared with bedrock groundwater, <br />other spoil springs and unaffected surface waters. Station 114 also shows comparatively high <br />manganese and high nitrate levels. <br />Spoil spring discharges as measured from Mine 1 and Eckman Park totaled approximately <br />3.25 cfs during the spring survey of 1997. Due to the small size of the flows the spoil spring <br />discharges from Mine 2 have no significant impact on Fish Creek. <br />EFFLUENT MONITORING <br />A number of sedimentation control structures at Mine 1 and 2 are monitored. Of these only <br />Stations 39 (Pond A), 84 (Pond D) and at Mine 1 had significant flows during the 1997 <br />irrigation season. Stations 57 (Pond H), 41, 87 (Pond F), (Pond K), and 91 (Pond M) showed <br />EP97TEXT.DOC 07/01/98 8 <br />