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2.8 Sample Container Cleanliness and Decontamination <br /> column. A low-Flow or low-permeability probe is defined as a condition where <br /> 1. New containers should be shown to be free of contaminants by providing data the minimum flow rate(100 mUmin)could not be sustained at the maximum <br /> from either the supplier or the analytical laboratory. applied vacuum level(I 0o inches water). See Appendix D for sampling <br /> protocols for low-permeability soils. <br /> follows: <br /> 2. After each use,reusable sample containers should be decontaminated as 3. Soil Gas Sample Collection using Sorbents for Method TO-17:Soil gas <br /> sampling for analysis by Method TO-17 is described in Appendix E and F. <br /> A. Glass syringes or bulbs should be disassembled and baked at 240°C for Low permeability materials may result in a lower Bow rate. Use of vacuum <br /> a minimum of 15 minutes o be d C fora minimum of 30 minutes,or be gage is recommended between the sorbent and extraction device. <br /> decontaminated by an equivalent method. If a syringe is re-used,it should Permeability testing of soil is recommended to determine the optimal flow rate <br /> be blank tested,and tested for adsorptive losses via spike testing. Blank at a vacuum of less than 100-inches of water(McAlary at a1:2009). TO-17 is <br /> testing frequency(or certification frequency)of syringes should also be currently recommended only for naphthalene analysis;however,TO-17 may • <br /> included in the workplan. also be used for other volatile constituents depending,on the DQOs for the <br /> project. The regulatory agency should be notifed and concurrence is <br /> B. SUMMA°canisters should be properly decontaminated as specified in US required prior to implementation of sorbent/TO-17 for other volatile <br /> EPA Method TO-15,and/or should be certified according to project DQOs, constituents other than naphthalene. <br /> either be batch or individually certified. 3.0 Field Conditions <br /> C. Tedlar`bags may be reused if data are provided to show the bags are Field conditions,such as rainfall,irrigation,fine-grained sediments,or drilling <br /> free of contaminants. <br /> conditions may affect the ability to collect soil gas samples. <br /> D. Equipment blanks should be analyzed to verify and evaluate the <br /> 1. Rainfall and Barometric Pressure(see Appendix Rainfall decreases <br /> effectiveness of decontamination procedures for recycled or reused the air-filled porosity of the shallow sail,thereby limiting <br /> diffusion transport of <br /> containers. At a minimum,one equipment blank should be run per 20 <br /> sample containers cleaned or at least one per day. volatile contaminants t so potentially biasing soil gas sampling results. <br /> Hence,do not conduct soil gas sampling during or within five days of a <br /> significant rain event(1/2 inch or greater). Stop irrigation or watering of soil at <br /> 2.9 Sample Collection least five days prior to the soil gas sampling event. Likewise,areas subject to <br /> soil gas sampling should be free of standing or ponded water for at least five <br /> 1. Vacuum Pump:When a vacuum pump is used,collect samples on the intake days prior to sampling. Do not perform soil gas sampling in swales or <br /> side to prevent potential contamination from the pump. Use a lung box when depressionswhere large volumes of water can potentially accumulate. <br /> collecting samples using Tedlar°bag(see Appendix C,Figure C-1). Record Barometric pressure Fluctuations associated with the passage of frontal <br /> vacuum readings and corresponding Flow rates on field data sheets for each <br /> sample.If the pump is battery operated,the batteries should be checked systems.can introduce atmospheric air into the shallow nodose zone. • <br /> before and during operation to insure a proper charge is maintained. Therefore,soil gas sampling should be delayed until Frontal systems have <br /> passed the area.Alternatively,soil gas sampling times and depths may be <br /> 2.. Soil Gas Sampling in Low-Permeability Soil:Soil gas sampling from low chosen to minimize the effects of changes in barometric pressure. <br /> permeability material(i.e.,silt and clay-rich soils)is feasible and high quality 2. Wet Conditions:If no-flow or low-Flow conditions are caused by wet soils due <br /> data can be produced with:(1)good annular seals;(2)careful monitoring of <br /> to a rain event or irrigation-flor water is drawn into a probe,cease the soil gas <br /> flow and vacuum during purging and sample collection;and(3)using tracer <br /> sampling. Low or no-flow condition corresponds to cases where the minimum <br /> gas i.e.,helium)for leak-testing. If the soil gas permeability is too low to flow rate of 100 mUmin cannot be sustained at the maximum applied vacuum <br /> allow sustainable purging at appreciable Flow rates without applying excessive <br /> vacuum,follow the protocols as described in Appendix D. An"appreciable of 100 inches of water(McAlary at al.,2009). If the low-flow condition is due <br /> flow rate"is defined as Flow of 100 mUmin or greater,and an"excessive to wet conditions or shallow groundwater,then passive samplers may be <br /> vacuum"is defined as any vacuum greater than about 100 inches of water deployed to detect VOCs. <br /> 3/3/2010 -29. <br /> 3/3/2010 -30- <br />