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2900 - Site Mitigation Program
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PR0536718
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Last modified
11/1/2018 7:14:07 PM
Creation date
11/1/2018 2:52:00 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0536718
PE
2960
FACILITY_ID
FA0021094
FACILITY_NAME
FORMER SIEBOLD CONSTRUCTION
STREET_NUMBER
820
Direction
S
STREET_NAME
AMERICAN
STREET_TYPE
ST
City
STOCKTON
Zip
95206
APN
14729211
CURRENT_STATUS
01
SITE_LOCATION
820 S AMERICAN ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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3. As an alternative to the Encore® sampler for laboratory analysis of VOCs, soil <br /> samples may be collected with a clean syringe. As per EPA Method 5035, a new <br /> plastic 10 ml syringe will have the bottom end removed,and the syringe will be <br /> inserted into the exposed soil until approximately five milliliters of soil is collected. If <br /> the soil is suspected to contain elevated levels of calcium, then a sample of the soil <br /> should be exposed to sodium bisulfate to test for effervescence. Calcareous soil <br /> samples may react upon contact with sodium bisulfate solution,causing VOC loss <br /> through effervescence and potentially cause failure of the VOA vial septum through <br /> pressure buildup. The soil must be field screened to determine if elevated <br /> concentrations of volatiles are detected,and the syringe samples must be collected <br /> within two hours of soil sample collection. The soil will then be extruded from the <br /> syringe into a laboratory preserved pre-weighed 40 ml glass vial.The vial caps must <br /> contain the special PTFE dual septa for the 5035 method. The vials will be preserved <br /> with either sodium bisulfate for low level concentrations of volatile constituents <br /> (detection limit<200 µg/kg),or methanol for elevated concentrations of volatile <br /> constituents(detection limit>200 gg/kg). Three vials will be filled from the single <br /> syringe for each laboratory sample collected.Each vial's label will be completed with <br /> the job number,the sample identification,date and time of collection,the sampler's <br /> name, and the analyses required. Each set of three vials will be placed into a sealed <br /> plastic bag or foam storage rack and then placed into an ice chest(chilled to 4°C) <br /> until delivered to a state-certified laboratory under chain-of-custody documentation. <br /> • A portion of the soil from the sample location will also be placed into a ziplock bag <br /> for lithologic logging and for field screening with an organic vapor analyzer(OVA), <br /> [such as a photoionization detector(PID), an organic vapor meter(OVM),or aflame <br /> ionization detector(FID)]. <br /> • Once the soil in the baggie has been allowed to sit for several minutes,the headspace <br /> of the baggie is screened for organic vapors with an OVA to document the presence <br /> or absence of vapors emitted from the soil. The OVA readings shall be documented <br /> on the field notes. <br /> • If UST piping has been removed,the soil beneath the piping shall be sampled at a <br /> frequency of 1 sample per 20 linear feet. The sample shall be collected, described, <br /> screened and documented in the same manner referenced above. <br /> Stockpile Sampling Activities <br /> • If a stockpile is to be sampled,the pile shall be measured and the approximate <br /> volume calculated. <br /> • In general, one discrete soil sample per 20 cubic yards of soil shall be collected. If the <br /> pile is large,composite sampling may be performed at a frequency of one sample per <br /> 100 cubic yards or more. The actual sampling frequency will be site specific. <br /> • Random sample locations within the stockpile should be sampled,but shall be <br /> representative of the stockpile material. <br /> • The sampler shall dig a minimum of 12 inches into the stockpile prior to collecting a <br /> SOP Soil Sampling for 5035 VOCs 3 of 5 August 2011 <br />
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