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1. Quality Assurance/Quality Control(QA/QC) additional quality control measures. Freshly packed or new sorbent tubes must be <br /> conditioned before use.Conditioning entails heating the tubes at specific <br /> The QA/QC requirements for Method TO-15 are different than that of EPA temperatures with a set gas Flow(See Table 2 of method). Tubes can be reused for <br /> Method 8260B/C. The calibration curve and tuning need to be checked every 24 multiple thermal desorption cycles until the"safe sampling volume"validation <br /> hours for Method TO-15 compared to every 12 hours for Method 8260131C. procedures fails(USEPA,1999,Method TO-17,Section 13.1.2). <br /> There are no requirements to verify the calibration curve with a second-source <br /> standard,to analyze matrix spikeimatrix spike duplicate samples(MS/MSD), For calibration,either gas(vapor)-phase or liquid standards can be used. Liquid <br /> laboratory control samples(LCS)or use surrogates for Method TO-15. standards are directly injected into the sorbent tubes for calibration. No calibration <br /> Consultants,regulators and other parties involved with using Method TO-15 for validation with gas-phase standards is needed if liquid standards are used. <br /> soil gas analysis may include additional QA/QC requirements not required by <br /> Method TO-15 to their testing protocol. Discretion should be used in deciding Furthermore,"sample tubes awaiting analysis on an automated desorption system • <br /> whether additional QA/QC will provide any additional data validation information. must be completely sealed before thermal desorption to prevent ingress of VOC <br /> contaminants from the laboratory air and to prevent losses of weakly retained <br /> 2. Autosamolers analytes from the tube."(USEPA,1999,Method TO-17,Section 8.2.1.2) <br /> Samples in passivated stainless steel canisters(i.e.,SUMMAIDs)can be analyzed Because of the manner by which gaseous samples are collected,this method has <br /> with an autosampler if the canisters are directly connected to the autosampler several inherent advantages over Methods TO-15 and 8260. One advantage is the <br /> without any further sample transfer. Additional blank samples should be included ability to collect and concentrate a larger volume of sample. Consequently,lower <br /> in the sample sequence to evaluate possible carryover of highly contaminated reporting limits can be achieved if the entire VOCs volume of sample trapped on the <br /> samples. sorbent tube is described completely as a single aliquot of sample. In comparison, <br /> only a smaller sub-sample is usually analyzed for TO-15 at a time;therefore,the <br /> 3. Canisters certification reporting limits are more elevated. <br /> Canisters used with EPA Method TO-15 must be certified clean with the same However,there are disadvantages in using TO-17. Some of the perceived <br /> data acquisition mode as the sample analysis. See Discussion on Scan vs.SIM disadvantages in using sorbent tube as a collection method include the inability to <br /> mode. repeat an analysis on the same sample,potential mass spectrometer(MS)overload <br /> due to desorption of concentrated sample and column breakthrough. The <br /> 4. Shipping of soil gas samples,especially in pressurized containers,by air should unfamiliarity of practitioners in handling and collecting soil gas samples onto sorbent <br /> be avoided. There are Federal restrictions on shipping pressurized containers by tubes is another potential disadvantage,since samples are mostly collected in <br /> air. Check with the shipper first if there is a need to ship such samples by air. canisters and syringes in the United Stales. Sorbent tubes are used less frequently <br /> Also consult with the federal code of regulations(49CFR,Parts 100-185)on for sampling in the:United States whereas they are used widely in the European <br /> specific regulations on the shipment and transportation of various materials. countries. <br /> C. EPA Method TO-17 With Method TO-15,additional analysis on the same sample can be easily • <br /> performed by withdrawing another sample aliquot from the sample canister. With <br /> EPA Method TO-17(Determination of Volatile Organic Compounds in Ambient Air Method TO-17,once all the compounds are desorbed from the sorbent tube,the <br /> Using Active Sampling Onto Sorbent Tubes, USEPA,1999)is another method sample is completely used. Repeating a sample analysis is possible only if multiple <br /> designed for collecting and analyzing VOCs in ambient air samples which is also (duplicate)sorbent tubes are collected. Multiple sorbent tubes can be collected <br /> used for soil gas analysis. A volume of air(or soil gas)is pulled through a sorbent concurrently if several sorbent tubes are manifolded in parallel during sampling. <br /> tube to collect the VOCs followed by thermal desorption of the VOC onto the GC Nevertheless,recent advances in thermal desorption(TD)technology have made it <br /> column for separation and analysis by the mass spectrometer. Other detectors or possible to split sample into fractions for repeat runs from the same sorbent tube. <br /> combinations of detectors such as ECD/FID in series can be used with this method <br /> provided that the criteria specified in Section 14 of the method are met. For quantification,the volume of air passing through the cartridge must be measured <br /> and documented. Moisture can be a problem with sorbent cartridges but it can be <br /> Method TO-17 is primarily a sampling method. Analysis of samples follows the managed by using alternative sorbents,sample splitting or dry purge(USEPA,1999, <br /> analytical approach in USEPA Method TO-15. The use of sorbent tubes requires Method TO-17,Section 7.2). The use of in-line water traps is not recommended <br /> 12/10/2009 -77- 12/10/2009 -78- <br />