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Decontamination may consist of steam cleaning or a three-stage wash and rinse tracer compounds are applied to towels or clean rags and placed around all <br /> consisting of a wash with a non-phosphate detergent,a rinse with tap water,and connections in the sampling train in order to evaluate potential leaks of ambient <br /> a final rinse with distilled water. Collect one equipment blank at the beginning of air into the sampling train.The leak check compound selected should not be a <br /> sampling,and at least one each day after decontamination. Air dry equipment suspected site-specific contaminant. <br /> prior to re-use. Use new or unused sample tubing for each probe location. <br /> Reuse of tubing is not recommended. Seal integrity is confirmed by analyzing subsequent soil gas samples for the <br /> tracer compound. Alternatively,gaseous tracer compounds,such as helium, <br /> isobutene,propane,and butane,can be used along with a shroud or tent over <br /> Sub-Slab Investigation Methods the sampling equipment.Procedures for conducting a quantitative leak test using <br /> helium as a tracer compound are described in Appendix C. <br /> • The procedure for collecting sub-slab soil gas samples are the same as for <br /> collecting sub-surface soil gas samples except that a slower flaw rate and lower Leak check compounds(i.e.,liquid tracer compounds)should be included in the <br /> vacuum should be utilized.Using a flow rate of less than or equal to 50 milliliters method analyte list. The laboratory reports should quantify and annotate all <br /> per minute(ml/min)and maintaining a low vacuum of less than 100 inches of - detections of the leak check compound at the reporting limit of the target <br /> water should prevent ambient air breakthrough into samples(McAlary at al., analytes. If the concentration of the leak check compound is greater than or <br /> 2009).Methods and procedures for installing sub-slab vapor wells are described equal to ten times the reporting limit for the target analyte(s),.then corrective <br /> in the DTSC Vapor Intrusion Guidance(Cal/EPA,2005, Page G-1) action is necessary as discussed below. <br /> 2.4 Solt Gas Sampling If a leak check compound(i.e.,liquid tracer compounds)is detected in the <br /> sample,the cause of the leak should be determined,evaluated,and corrected <br /> Before obtaining soil gas samples,leak and purge volume tests are necessary. through retesting. If a leak is confirmed and the problem cannot be corrected, <br /> the ambient air leak may be quantified using a gaseous tracer with a shroud,as <br /> Leak Test described in Appendix C. An ambient air leak up to five(5)percent is acceptable <br /> if quantitative tracer testing is performed by shrouding. Otherwise,the soil gas <br /> A leak lest is used to evaluate whether a good seal was established in the vapor well should be decommissioned if the leak cannot be corrected. <br /> sampling train,ground surface,and probe interface. A leak test should be Replacement vapor wells:should be installed at least five(5)feet from location <br /> conducted at every vapor monitoring well each time a soil gas sample is where the original vapor well was decommissioned due to a confirmed leak. <br /> collected because a poor seal may result in soil gas samples that are diluted by Include the leak check compound concentrations detected in the soil gas <br /> ambient air.This may result in an underestimation of actual site contaminant samples in the laboratory report and discussed in the site characterization report. <br /> concentrations or,alternatively,introduce external contaminant into samples from <br /> ambient air. Note that if sampling is done exclusively from a SUMMe canister at a stationary <br /> laboratory and there is a significant leak,it will not be identified until after the <br /> Shut-In Test:Prior to purging or sampling soil gas,a shut-in test should be sample has been collected and analyzed. Therefore,field screening prior to <br /> conducted to check for leaks in the above ground fittings. The shut-in test laboratory confirmation is recommended. <br /> consist of assembling the above-ground apparatus(e.g.,valves,lines and fittings <br /> downstream from the top of the probe),and evacuating the lines to a measured <br /> vacuum of about 100 inches of water column(in-H2O),then shutting the vacuum 2.5 Purge Volume Test <br /> in with closed valves on opposite ends of the sampling train. The vacuum gauge <br /> connected to the line via'T"-fitting is observed for at least one minute,and if The purpose of a purge volume testis to ensure stagnant or ambient air is <br /> there is any observable loss of vacuum,the fittings are adjusted as needed until removed from the sampling system and to ensure samples collected are <br /> the vacuum in the above-ground portion of the sample train does not noticeably representative of subsurface conditions. The purge volume test should be the <br /> dissipate(McAlary at al.,2009). first soil gas sampling activity at the selected purge volume test point,and should <br /> be located as near as possible to the anticipated or confirmed contaminant <br /> Leak Check Compounds:Liquid tracer compounds,such as hexane,pentane, source,and in an area where soil gas concentrations are expected to be <br /> and n-propanol,can be used to evaluate the sample integrity. Typically,liquid elevated,based on lithology.The purge volume lest is conducted by collecting <br /> and analyzing a sample for target compounds after removing one,three,and ten <br /> 3/3/2010 -23- 3/3/2010 -24- <br />