Laserfiche WebLink
10 <br /> 6. Prior to collecting the sample in the canister, collect a sample in a 1-liter Tedlar bag. <br /> Analyze this Tedlar bag sample with the handheld detector for the tracer gas and with <br /> the helium detector and record the concentrations detected. If the concentration of the <br /> tracer is >10% of the concentration which was measured from the shroud, the probe <br /> should be re-sealed. The tracer test will be performed again, and sample collection <br /> will proceed when the tracer concentration is<10%. <br /> 7. Following collection of the sample in the Summa canister, an additional soil gas <br /> sample will be collected in a Tedlar bag and monitored for helium. If both the pre- <br /> and post-sampling Tedlar bag samples contain helium at <10% of the shroud <br /> concentration, then the sample will have passed the leak test. If not, additional <br /> corrective measures will be taken in the field (e.g., tightening fittings) and the test <br /> will be repeated. If the<10%criteria cannot be met at a given probe, that location and <br /> depth will be eliminated from the validation program. <br /> Soil Gas Ambient Air Leak Detection Protocol using Duster <br /> The real time leak testing procedures using the "duster" as the tracer compound will be <br /> accomplished as follows: <br /> 1. Place a shroud over the annulus of the soil gas sampling probe. The sampling tube should <br /> extend out of the opening in the top of the shroud. Press the top of the shroud into the soil <br /> to achieve a seal. Alternatively if sampling through a hard surface, prepare a seal of <br /> hydrated bentonite around the bottom edge of the shroud (see diagram on following <br /> page). <br /> 2. Attach a standard handheld refrigerant leak detector used in the automotive industry to <br /> the soil gas sampling tube using appropriate fittings. Automotive Freon leak detectors <br /> will not respond to non-halogenated VOCs such as benzene. Tum on the refrigerant leak <br /> detector (knowing the pump rate of the detector) and time the detector to purge <br /> approximately three casings volume of soil gas. High levels of halogenated VOCs present <br /> in the soil gas may trip the detector. If a response to the soil gas is noted, reset the <br /> instrument for background concentrations. <br /> 3. Spray into the open shroud a "Duster", "Dust-off' or "Computer Duster" compound. <br /> Most are either difluoroethane or tetrafluoroethane and both will respond to the <br /> refrigerant detector. A second detector can be used to insure adequate "Duster" is added <br /> to the shroud (the instrument should give the maximum reading). Record the <br /> concentration of the tracer in the shroud. The Freon in "Duster" is heavier than air and <br /> can persist up to 30 minutes in the shroud in calm air. Under windy conditions the former <br /> bottom of the shroud can be used to shield the duster from the wind. Collect a soil gas <br /> sample in a Tedlar bag and screen it for the tracer. A failed well annulus will be noted by <br /> a response from the detector either above background readings or above detection levels. <br /> A failed well annulus may be corrected by replacement/rehydration of the bentonite seal <br /> of the soil gas probe or by checking for a possible "short circuit" of ambient air through <br /> the soil or sub-grade (such as asphaltic concrete sub-grade). Soil gas probes that continue <br /> to leak at the annulus should be abandoned and moved to an adjacent location. Record all <br /> screened concentrations. <br />