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EPA DESCRIPTION REVISIONS(DATE) COMMENTS introduction(i.e.,direct injection,purge-and-trap,vacuum distillation,automated <br /> METHOD static headspace and cartridge desorption),none of which were designed for soil <br /> Mamas.D wase new as. For soil as samples,modifications of the introduction step are needed. <br /> volatile organic compaaaaw NOGsY N melted amen w s a newad 9 9 P P <br /> Ar Collective sped roy-Repered Edldon'or ther'Compendian of Based on surveys conducted by DTSC of fixed and mobile laboratories that <br /> Tats CeNstes and Metyaed By Gas 'Second Ef ilbn• M ema is fame Dmermltmdon analyze soil as samples,there are two basic techniques that are current) dein <br /> Cbomaagraphy"Ims spectrometry (Jandery 1999) f Toxic Organic Compounds in Y 9 P 9 Y g <br /> (comes) AmbientW it Asplmoga employed for soil gas analysis using Method 8260B/C: purge-and-trap and direct <br /> Marland TO 14A. injection. Each sample Introduction technique has its own advantages and <br /> disadvantages. The advantages and disadvantages of each sample introduction <br /> Merhnd TO n ase tgw technique are summarized in Table 2. <br /> marled added a me'becand <br /> voltage Organic Compounds tunics)bEdilm•of the Yemperidlum d <br /> • Tan Ambient Ay hired Aaroe sampling Onto -Second Ealbn Merndds for the beamdabn Table F-2: Advantages and Disadvantages of Sample Introduction Techniques <br /> Sabena Tubes lamely 1999) of Toxic Organic compounds In <br /> Ambient Air'It is an update of sample ingodums. Advantages Olsadvanlages cammems <br /> Mehads TO I and TO-2 from Tac tie <br /> the l''vst cmmpendlum r 989). A volume of will gas longer volumes of sial Analytes are rated into e. • N r) omommenmd for <br /> sample Is Nkcted gas sempb may be water meed and impar out 1, polarA ater soluble <br /> (daces)Nm a Pageamforced Nm ware to Into trap before entering into comiewmars. <br /> trepspargerconulnitg achieve lower rapoding GC column.Loss of larger • Surrogates(liquid <br /> ..Aaalpas are wharswtunilmiatera. aneMes possible. phased)are used but <br /> purged out a apager low sum Antes,Internal Depending on fire type m Introducetl separately <br /> too vabma trap us, vanderm and spkes sample conaalnelNesset In Into sperger.Does nag <br /> Helium gas.Antras in are added immune which the sample le actually reskim file <br /> F-3 MODIFIED GCIMS METHODS the hep ere thermally Vargas before temple collected,sample may meed OMQC thin.to wll gas. <br /> descried Ino the GC NfioduUbn and In be vanareaed beret . Ideal for rather <br /> column fa separation. WON awthan Imo quarter- cere.nterbn samples. <br /> A. EPA Method 8260 soil gas volumes can pmami.I wrize lessor • Nouatommemed fa <br /> bar changed by using a oweJor praew. few level pant' <br /> smaller syringe or Low recovery of pobrAverer ctrcerwamm samples. <br /> EPA Method 8260(Volatile Organic Compounds by Gas Chromatography/Mass teentated sial gas actual.wmpaends. . Recommended for <br /> Spectrometry GCIMS Is designed to determine VOCs in a variety of solid and wrmpas can bB cubed c.11badaa cave cot aacemng a mygerams <br /> P ry( )) 9 Y in glass bulb before mamntmduad n actino a cblorbatm <br /> liquid matrices(SW-846,1996). There are two basic technical modifications made dlaadgirmmnger. standards ane used. compounds due to poor <br /> to this analytical method for soil gas sampling. In the first technique,a volume of soil ` size; aBd <br /> as sam le is in ected into the s ar a vessel(s ar er containin water and then sand le iia Gcomlumnn gas O ated s mue ple ne dlllth. WeeasaMdld lmitilan bw much Recommended! <br /> cre�eni g pumfa <br /> 9 P 1 r 9 P 9 ) 9 p ^g "9 dead an <br /> VOCs are purged out the sponger with helium gas onto a sorbent trap. VOCs in for s.pere"°" Haulag aIle=not an wmptcwm fo/aaadima (gtwnuaM=mal and <br /> the sorbent tri are thermal) deserted into the GC column for separation and he.pmvded samples GC column. aadata monato ng of <br /> P Y P mspgd immediately . Loam mucking M,ns may dmul number of known <br /> analysis. This is equivalent to EPA Method 5030(Purger-and-Trap for Aqueous wer"60dn. hot has pasalble am ma compounds. <br /> Samples). In the second technique,a small volume of the soil as sample is directly Na taawreaaenaiyles may not meet the DOOs fa CeYbabn sandarm <br /> P 9 9 P Y from as phase to risk athwarert purave; pa.,.d by wromalan <br /> injected into the GC. It analxr(I.e..gas 1. calibaatbn not mama of iquid standards In <br /> liquid to gas), meshed. vialsbulb may rot be <br /> Can handle high level ameaahle to ea <br /> Laboratories employing a modification of EPA Method 8260 to analyze soil gas maeearmed)sampa, caargaunds. <br /> samples should adhere to all the basic analytical requirements of the original method <br /> including purge time,calibration and Quality Assurance/Quality Control(QA/QC). <br /> `Modifications for soil gas samples are outlined in the following sections. 2. Calibration <br /> Either EPA 8260B or 8260C is acceptable. 8260C is an updated version of 82608. a. One of the limitations of using EPA Method 82608 for soil gas analysis is <br /> Because the California certification program(E LAP)does not currently certify labs to the calibration technique. The current practice in most laboratories is to <br /> do 8260C,labs are certified for 82608 only. use liquid-phase standards to prepare the calibration curve. For logistical <br /> 1. Sample Introduction and economic reasons,soil gas calibration curves are prepared with <br /> liquid-phase standards. The use of liquid-phase standards may create <br /> The original EPA Method 8260 outlines five specific methods for sample biases which are undetermined. The chemical dynamics(vapor pressure, <br /> solubility,etc.)of each compound is different. The"behavior"of a <br /> 12/10/2009 -71 - 12/10/2009 -72- <br />