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C. If the soil gas data are to be used to support risk assessment <br /> activities, a DL of 1 µg/L may be appropriate for the initial <br /> screening when evaluating all targeted VOCs. If the data are non- <br /> detect for all targeted VOCs, additional sampling with lower DLs is <br /> not required. If VOCs are detected, additional sampling, using a <br /> DL of 0.1 µg/L, may be required to confirm the non-detection of <br /> carcinogenic VOCs[see the Toxicity Criteria Database of the <br /> California Environmental Protection Agency, Office of <br /> Environmental Health Hazard (OEHHA), or the Integrated Risk <br /> Information System (IRIS) Database of the United States <br /> Environmental Protection Agency]. A DL of 0.1 µg/L may be <br /> proposed and used for all carcinogenic target VOCs from the <br /> beginning of the investigation. <br /> D. Based on site-specific DQO needs, lower DLs may be required. <br /> Examples of sites requiring site-specifc DQO needs include, but <br /> are not limited to, chlorinated solvents sites,former industrial <br /> facilities and landfills. Several less common VOCs, not included <br /> on the ASGI-targeted compound list, may require lower detection <br /> limits[e.g., bis(chloromethyl)ether, DBCP (1,2-dibromo-3- <br /> chloropropane), or ethylene dibromide]when they are known or <br /> suspected to be present. <br /> E. If the required DLs cannot be achieved by the proposed analytical <br /> method, additional sample analysis by a method achieving these <br /> DLs[e.g., EPA Method 82606 with selective ion method (SIM), <br /> TO-14A, TO-15] may be required. Use of these methods should <br /> comply with the QA/QC requirements as specified in Section <br /> 2.7.1. <br /> F. For results with a high DL reported (e.g., due to matrix interference <br /> or dilution), the laboratory should provide a written explanation. <br /> Re-sampling and analyses may be required at the appropriate DL <br /> for a specific compound. <br /> 2.7.4 Sample Handling: Exposure to light, changes in temperature and <br /> pressure will accelerate sample degradation. To protect sample <br /> integrity: <br /> A Soil gas samples should not be chilled; <br /> B. Soil gas samples should not be subjected to changes in ambient <br /> pressure. Shipping of sample containers by air should be avoided; <br /> and <br /> C. If condensation is observed in the sample container, the sample <br /> should be discarded and a new sample should be collected. <br /> 01/28/2003 - 16- <br />