Laserfiche WebLink
Mr. Bryce Romig • 2 • September 9, 1996 <br /> • Analysis of total recoverable iron and total recoverable manganese may be analyzed <br /> on an intermittent basis only, depending on total suspended solids (TSS) and <br /> dissolved iron and manganese concentrations in the reservoir water. Dissolved iron <br /> and dissolved manganese will continue to be monitored. <br /> Sampling Events and Analyses <br /> Each sampling event included collecting one composite soil sample from the reservoir <br /> bottom material and obtaining surface water samples from the reservoir. The surface <br /> water samples were collected prior to complete removal of the tailings to determine what <br /> analytes are present and to assess water quality under worst-case conditions. Soil <br /> samples were collected in areas where tailings had been removed to obtain baseline metal <br /> concentrations of the remaining bottom material in the reservoir. <br /> Sampling procedures followed are outlined in the SAP. To provide Quality Assurance/ <br /> Quality Control (QA/QC), one split surface water sample was analyzed per sampling <br /> event. Field pH, conductivity, temperature, and dissolved oxygen measurements were <br /> also taken in the field for the water samples. Laboratory analyses were conducted on the <br /> surface water samples for parameters regulated by the Colorado Department of Health <br /> (CDH), Water Quality Control Commission(see Tables 1 and 2). Water quality standards <br /> • for each sample were calculated based on water hardness as outlined by the CDH and are <br /> also included in Tables 1 and 2. The standards were calculated using the most <br /> conservative hardness value per sampling event. For the May event, a hardness value of <br /> 658 mg\L as CaCO3 (sample SW-2) was used, and for the July event, a hardness value of <br /> 491 mg\L as CaCO3 (sample SW-I) was used. Total metal concentrations in soils were <br /> determined by laboratory analyses (see Table 3). <br /> During the May sampling, approximately one-third of the original tailings remained in <br /> the Eagle Park Reservoir. Excavation had been delayed due to high water levels in the <br /> reservoir which formed two large ponds to the east and west of the access road. Water <br /> was being pumped from the east pond, causing some flow over the road from the west <br /> pond. Three water samples were taken from the west pond (two near the dam and one <br /> near the road), and one sample was taken from the east pond. The split sample was taken <br /> from a sample on the west side, near the north side of the dam. A composite of three soil <br /> samples was collected from locations on the south side of the west pond. <br /> The water level during the July sampling was significantly lower than during the May <br /> sampling. The remaining tailings near the dam were being excavated. Water in the <br /> reservoir existed in four shallow (4 to 6 feet) disconnected ponds. Samples were taken <br /> from two ponds near the dam face and from a pond on the east side of the access road. <br /> The split sample was taken from a sample near the north side of the dam face. Because of <br /> the low water to tailings ratio (especially near the dam face), these water samples are <br /> ---- �— <br /> C:\PROJECTS\6102-001\T1696102.00I[9-Sep-96] Environmental <br />