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U U <br /> City of Stockton <br /> A68107.07A <br /> May 29, 1996 Page A-3 <br /> • During groundwater sampling, a travel blank sample consisting - <br /> P g of or ganic free � <br /> water is prepared and containerized in the laboratory, transported to the site, <br /> and handled and transported in the same manner as the groundwater samples. <br /> A-5 Standard Operating Procedures for Using Photoionization Detector(PIP): 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. The background concentrations are measured <br /> f in a location upwind and removed as possible from sources of organic vapors on the site. <br /> When background concentrations of organic vapors register as "0.0" on the PID, subsequent <br /> readings of "0.0" registered from samples tested in the field are recorded as "ND" (not <br /> detected). When background concentrations of organic vapors register at some quantity <br /> i3 above "OA", subsequent readings registered from samples tested in the field at or below this <br /> value are recorded as "B/G" (background). <br /> A-6 Standard Operating Procedures for Performing Head Space Anal sis: Head space <br /> analysis is performed using a photoionization detector (PID) or a drager tube. A soil <br /> t sample is placed in a sealed glass container or plastic bag, agitated, and placed in a warm I <br /> L� atmosphere. After approximately 15 minutes, which is generally sufficient for some of the <br /> volatiles to escape from the soil, the PID probe or tip of the drager tube is inserted into the <br /> container or the bag and air above the sample is pumped into the PID or drager tube. The <br /> highest concentration of organic vapors recorded by the PID or the drager tube reading will <br /> r <br /> be recorded. <br /> a <br />