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Marcb 2007 Hayrien Gulcb I~arlau! - 2006 Annual <br />3.0 HYDROLOGIC MONITORING <br />3.1 SAMPLING AND MEASURING TECHNIQUES <br />Field measurements were recorded for conductivity, pH and temperature. Surface water flow was <br />measured with a Swoffer Mode12100 portable velocity meter, or visually estimated. Static groundwater <br />level measurements were taken with an electronic water level indicator. <br />Field conductivity and pH meters were calibrated prior to each days use. The conductivity meter was <br />calibrated using a potassium chloride solution with an electrical conductivity in the 413 to 6,668 miao- <br />Siemens per centimeter (µS/cm) range. The pH meter was calibrated using NBS traceable buffers <br />with pH values of 7.0 and 10.0 units. <br />Surface water and groundwater samples collected for laboratory analysis were collected using standazd <br />industry practices and U.S. Environmental Protection Agency guidance to assure the data is <br />representative of the water resource being observed. Table 1, CDPS Permit COG-850008 Analytical <br />Lirt, presents the pazameter list Eor the sediment pond outfall samples. Table 3, Surface Water Analytical <br />Lirt, shows the laboratory analyses for the surface water samples. Table 4, GmundwaterAnalytical List, <br />presents the laboratory analyses foz the groundwater samples. Analyses were performed by ACZ <br />Laboratories, Inc. (ACZ) of Steamboat Springs, Colorado. ACZ performs all analyses by U.S. <br />Environmental Protection Agency (EPA) or equivalent methods. <br />The surface water analytical suite was modified during 2005 as pazt of Technical Revision No. 6 (TR- <br />O6), which the CDRMS approved in June, 2005. The analytical suite was modified as part of TR-OG to <br />assure compliance with CDPHE regulations which were amended in January 2004 (Regulation 33) and <br />Mazch 2005 (Regulation 31). With the approval of TR-06, sample analyses For aciditp, aluminum, <br />barium, fluoride, molybdenum and phosphate have been discontinued because these pazameters aze <br />not listed in the stream standazds set forth by the CDPHE in Regulation 33, Classification and <br />Numeric Standazds Eor Upper Colorado River Basin (Yampa Rives segments 13d and 13e). There aze <br />also no agricultural standazds for these constituents in Regulation 31, Basic Standards for Surface <br />Water. The "analytical technique" for cadmium, copper, lead, manganese, nickel, selenium, silver and <br />zinc has been changed from "total recoverable" to "potentially dissolved." This is the technique <br />mandated by the CDPHE in Regulations 31 and 33. For similar reasons, the form of iron analyzed <br />was changed to "total recoverable." Finally, the analytical technique fot mercury is total, not "total <br />recoverable" as had been reported in previous annual hydrology reports. <br />3.2 SURFACE WATER DATA <br />3.2.7 Colorado Wastewater Discharge Permit System (CDPS) Monitoring <br />There aze two sediment ponds that aze regulated in accordance with the Colorado Wastewater <br />Discharge Permit System. The ponds aze identified as the Truck Loop Pond (Outfall OOlA), and the <br />Rail Loop Pond (Outfall 002A). The locations of the two sediment ponds aze shown on Figure 1, <br />Manitanng Site Lacationr. <br />Discharge from both ponds was observed in 2006 for the fast time in several yeazs. Table 2, Summary <br />of Sediment Pant CPDS Manitanng, presents a summary of the CDPS monitoring observations for 2006. <br />Appendix A, CDPS Water Quality Data, includes a listing of water quality statistics for the Loadout <br />CDPS sites. <br />Hydro-Environmental Solutions, Inc. <br />P.O. Box 772996 <br />57 108 Street, Suite B <br />Steamboat Springy, CO 80477 <br />(970) 871-6125 <br />