Laserfiche WebLink
City of Stockton A68104 01A <br /> October 25, 1995 Page A-6 <br /> laboratory in Fresno, California Analytical methods with corresponding method detection <br /> limits and copies of the chain-of-custody records are be provided in the technical report <br /> A-7 Laboratory Quality Assurance/Quality Control (OA/QC) This section describes the <br /> laboratory QA/QC procedures which are followed during the analyses of the soil and <br /> groundwater samples by Twining's analytical chemistry laboratory <br /> The QA/QC procedures are developed to minimize outside interferences during analyses <br /> for each sample The laboratory manager is in charge of creating and maintaining the <br /> program In general, QA/QC proposed for this investigation are summarized as follows <br /> ■ Analytical instruments are serviced on a regular basis to monitor accurate calibration, <br /> Y <br /> ■ Organic-free water is monitored daily for quality, <br /> ■ Gas chromatographs are calibrated daily, <br /> ■ Method blanks are tested to check whether the lassware and reagents are free of <br /> g <br /> interference from chemicals that would invalidate the analyses, and <br /> ■ Standards are prepared using the applicable reference materials <br /> A-8 Disposal of Rinsate and Soil Cuttings The soil cuttings generated by the drilling <br /> operations are sealed in 55-gallon United States Department of Transportation (DOT) <br />�j approved steel drums The augers and sampling equipment are cleaned on racks and the <br /> rinsate subsequently be transferred to 55-gallon DOT approved steel drums The drums are <br /> temporarily stored on site at a location remote to the public Each drum is labelled to <br /> identify its contents The disposal of this material will be the responsibility of the client <br /> This material must be disposed of in accordance with all applicable Federal, State and Local <br /> regulations Cost of disposal of this material range from $65 00 to $100 00 a ton not <br /> including transportation and management fees <br /> A-9 Standard Operating Procedures for Using Photoianization Detector(PID) The PID <br /> is calibrated in accordance with the manufacture's recommendations prior to use in the field <br /> Upon arrival at the project site, the PID is used to monitor background concentrations of <br /> organic vapors in the atmosphere at the site <br /> The background concentrations are measured in a location upwind and removed as possible <br /> from sources of organic vapors on the site When background concentrations of organic <br /> vapors register as "0 0" on the PID, subsequent readings of "0 0" registered from samples <br /> tested in the field are recorded as "ND" (not detected) When background concentrations <br /> of organic vapors register at some quantity above "0 0", subsequent readings registered from <br /> samples tested in the field at or below this value are recorded as "B/G" (background) <br />