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* N im vERMCATION LABORATORY 'L SIS <br /> TANK TANK TPH-G TPH-D BTX & E C 0 C TOTAL EDB T�� 82 0 <br /> PCB <br /> # CONTENTS 8065 8015 8270 8240 7420 8240 AFS or 8080 <br /> 37 sz6o az6o gz6o <br /> 7421 AA <br /> - <br /> LEADEDX X X <br /> GAS X <br /> UNL GAS X X <br /> DIESEL X X <br /> KEROSENE X X <br /> UNK FUEL X X X X X <br /> PROD. OIL X X <br /> CHLOR <br /> SOLVEN'T'S X X <br /> NONCHLOR <br /> SOLVENTS X X X <br /> WASTE\ <br /> USED OIL X X X X X X <br /> All analyses methods are designated EPA methods described in EPA SW 846, Third Edition. Those methods not found <br /> in SW'846, are specifically noted below. Refer to the 'SWRCB LUFT Feld Manual', Appendix A-20, Table 3-5 for <br /> detection limits of motor vehicle fuels (gasoline and diesel). Refer to 1-2-3 'Regional Board Staff Recommendations for <br /> Inidal',Evaluation and Investigation of USTs' for the waste and motor oil detection limits. <br /> Detection Limits that remain below the MCL, STLC or Allowable Limit of the contaminant in question will be accepted, <br /> however laboratory shall ndllze the most consetyative method. <br /> LABORATORY ANALYSES TERMINOLOGY: <br /> TPH-G Total Petroleum Hydrocarbon, Gasoline, GC/FID (5030) 8015 mod or GC/MS 8260 <br /> TPH-D Total Petroleum Hydrocarbon, Diesel, GCIFID (3550), 8015 mod oYGC/MS 8260 <br /> BTX &E Benzene, Toluene, Xylene & Ethyl Beaune, GC/PID 80M or GC/MS 8260 <br /> CL HC Chlorinated Hydrocarbon, GC/HSD 8010, GC/MS 8240 <br /> TOTAL LEAD Total lead, AA 7420, AA 7421 or ICP-AFS 6010 <br /> EDB Ethylene dibromide (DHS-AB 1803), GC/MS 8240 (DHS-LUFT) <br /> GC-FID Gas Chromatography, Flame Ionization Detection <br /> ICRP or AA Inductively Coupled Plasma Atomic Emission Spectrometry 6010 or Atomic Absorption <br /> Spectrometry 7000. Metals: Cadmium, Chromium III and VI, Lead, Zinc and Nickel. <br /> PCB Polychlorinated Biphenyls, GC/MS 8270 or 8080 <br /> Method 3050 Acid digestion <br /> Method 3540 Soxhlet sample preparation <br /> Method 3550 Sonication sample preparation, extraction method <br /> Method 5030 Purge and trap sample preparation <br /> QA/QC Quality Assurance/Quality Control <br /> Notes: To avoid false positive detection of benzene, benzene-free solvents are to be used. Fused capillary columns are <br /> preferred to packed columns; a packed column may be used as a 'first cut' with 'dirty' samples or once the hydrocarbons <br /> have been characterized and proper QA/AC is followed- <br /> For Drinking water sources, EPA recommends that the 500 series for volatile organics be used in preference to the 600 <br /> series because the detection limits are lower and the QA/QC is better. Samples exhibiting any level of heavy metal <br /> contamination may require further analysis. PHS-EHD recommends holding these samples until disposal is indicated. <br /> EH 23 048 (Revised 7/10/92) Page 8 <br />