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SAN J OAQ[YI N LOCAL HEALTH .,,D I S'I`R = CT <br />Y .:vie &. v xmir.VQTR <br />MINIMUM VERIFICATION LABORATORY ANALYSES TERMINOLOGY <br />The followyiing listin of laboratory <br />) analyses abbreeyvvsiations is provided as a guide so that <br />describedd In FPA SW1846, ThirdfEdition. Thosenmethodses mnotofoundeIn SW designated EPA <br />methods as <br />specifivally noted. <br />OR)8240 <br />B boa) <br />OR AA <br />Total Petroleum Hydrocarbon, Gasoline <br />Total Petroleum Hydrocarbon, Diesel <br />Total Extractable Petroleum Hydrocarbon (8015] <br />Benzene, Toluene, Xylene & Ethyl Benzene (8020) <br />nvArnrarhnn 8010 or 8240 <br />a dibromide •(DOHS -A$ 1803) <br />omatoaphy Flame Ionization Detector <br />gr <br />velv C uvltA Plasma Atomic Emission Spectrometry or Atomic <br />Method 5030 Purge ara rxap sam re rce lal=� <br />Method 3550 Sonication Sample repara ion <br />Method 3590 Quality Sample Preparation <br />rance/Quality Control <br />QA/QC Y Ass <br />Notes: To avoid false positive detection of benzene, benzene -free solvents are to be used. <br />Fused capillary columns are preferred to packed columns; a packed column may be used as a <br />"first cut" vith "dirty" samples or once the hydrocarbons have been characterized and <br />proper QA/OC is followed. <br />For Drinking Water Sources EPA recommends that the 500 series for volatile <br />organics be used In preference to the 600 series because the detection limits are lover and <br />the QA/QC Is better. <br />EH 23 048 12/88 <br />1'111Y1 <br />pVl"1 Yl-laCaw�a.+.• <br />.+••---•--- <br />EDB <br />METALS <br />-- -:.... <br />PCB <br />TANK CONTENTS <br />Waste Product <br />TPH-0 <br />OC FID <br />TPH-D <br />OC -FID <br />TEPH <br />3550) <br />BTX&E <br />(8020) <br />CL HC <br />(8290 <br />( <br />TEL <br />D <br />H 3) <br />()ICp- <br />AES) <br />(8270) <br />or--- <br />( 5030) <br />(15'5_0) <br />_ <br />LEADED GASOLINE <br />X <br />X <br />X <br />--- <br />-.---- <br />UNI, GASOLINE <br />X <br />X <br />--- <br />-- <br />-- -- <br />DIESEL <br />— <br />X <br />KEROSENE -- <br />— -- - <br />X <br />X <br />-- <br />-- <br />UNKNOWN FUEL <br />---- <br />X <br />---- <br />-- <br />X <br />X <br />-- <br />---- <br />OIL <br />X <br />X <br />— <br />--- <br />------ <br />— <br />CHLOR. SOLVENTS <br />X <br />X <br />NONCHLOR. SOLVTS <br />X <br />..--WASTENSED <br />L—L-i <br />--- <br />OIL <br />X <br />X <br />X— <br />MINIMUM VERIFICATION LABORATORY ANALYSES TERMINOLOGY <br />The followyiing listin of laboratory <br />) analyses abbreeyvvsiations is provided as a guide so that <br />describedd In FPA SW1846, ThirdfEdition. Thosenmethodses mnotofoundeIn SW designated EPA <br />methods as <br />specifivally noted. <br />OR)8240 <br />B boa) <br />OR AA <br />Total Petroleum Hydrocarbon, Gasoline <br />Total Petroleum Hydrocarbon, Diesel <br />Total Extractable Petroleum Hydrocarbon (8015] <br />Benzene, Toluene, Xylene & Ethyl Benzene (8020) <br />nvArnrarhnn 8010 or 8240 <br />a dibromide •(DOHS -A$ 1803) <br />omatoaphy Flame Ionization Detector <br />gr <br />velv C uvltA Plasma Atomic Emission Spectrometry or Atomic <br />Method 5030 Purge ara rxap sam re rce lal=� <br />Method 3550 Sonication Sample repara ion <br />Method 3590 Quality Sample Preparation <br />rance/Quality Control <br />QA/QC Y Ass <br />Notes: To avoid false positive detection of benzene, benzene -free solvents are to be used. <br />Fused capillary columns are preferred to packed columns; a packed column may be used as a <br />"first cut" vith "dirty" samples or once the hydrocarbons have been characterized and <br />proper QA/OC is followed. <br />For Drinking Water Sources EPA recommends that the 500 series for volatile <br />organics be used In preference to the 600 series because the detection limits are lover and <br />the QA/QC Is better. <br />EH 23 048 12/88 <br />