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2900 - Site Mitigation Program
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PR0536718
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Entry Properties
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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be provided by the laboratory. The laboratory using the modification must <br /> validate the procedures before implementation. The validation data and <br /> 5. Puree Time report should be made available for review by all affected parties. If needed, <br /> the Department of Toxic Substances Control's(DTSC)Environmental <br /> EPA Method 8260B specifies a purge time of 11 minutes. Laboratories Chemistry Laboratory(ECL)should be consulted on modifications. <br /> should not deviate from this specification as the method has been optimized <br /> for the recovery of all target analytes. If modifications are needed,they B. EPA Method TO-15 <br /> should be documented and validated. Validation should be performed with <br /> vapor-phased standards. EPA Method TO-15(Determination of Volatile Organic Compounds(VOCs)in Air <br /> Collected in Specially-Prepared Canisters and Analyzed by Gas Chromatography/ <br /> • 6. Aulosamplers Mass Spectrometry(GGMS))is traditionally used to analyze for VOCs in ambient air <br /> samples(USEPA, 1999). Samples are collected into specially prepared stainless <br /> The utility of using an autosampler with modified EPA Method 826OB/C is steel canisters. VOCs in a known volume of sample are concentrated onto a solid <br /> questionable. This practice is not recommended since:there.will likely be sorbent trap,and refocused on a second trap before being thermally descrbed onto <br /> sample loss during the sample transfer as well as possible leakage from the the GC column for separation. <br /> vials during the sample run. In addition,the vials may sit in the autosampler <br /> for an extended period of time. There are two techniques for introducing whole air samples by TO-15 from the <br /> canister into the gas chromatograph:(1)mullisorbent pack method;and(2)a <br /> 7. Screenino concentrator where the VOCs are condensed on a reduced temperature surface <br /> (i.e,,cold trap). For the multisorbent pack method,there are different types of solid <br /> Laboratories should screen samples(e.g.,with GC/FID),where possible, sorbent trap available depending on the compounds of interest. Traps with different <br /> before analysis to avoid saturation of the mass spectrometer. This will also type of sorbent packing have different retentive properties which can be used to <br /> provide information on the proper dilution(s)needed for quantification. selectively concentrate analytes of interest. <br /> 8. Data Review Laboratories employing EPA Method TO-15 to analyze soil gas samples should <br /> -- - adhere to all the basic requirements of the method including calibration and QA/QC <br /> Soil gas data generated with EPA Method 82608 should be reviewed in detail protocols.Method TO-15 is best suited for soil gas analysis since it is designed for <br /> to ensure that all QA/QC parameters are within specified control limits before gas samples. However,there are other modifications referred to as TO-15,which <br /> they are to beusi.for risk assessments/management or other critical are described in Table 3. The advantages and disadvantages of these modifications <br /> decision making purposes. are summarized below. Note that some of the modifications are not in technical <br /> compliance with the method. <br /> 9. Applicability <br /> Table F-3: Advantages and Disadvantages of Modifications <br /> • Modified Method 8260B works well for soil gas samaples with high MMlfletabn Haeme obeaama con ommis <br /> concentrations of VOC(i.e., >0.1 pg/L or 100 pglm)and for most samplas eolmcmd m . L.cos, slgnr m beckgeuM loeyasl. N«recommencen. <br /> compounds. However,this method may not be ideal for more polar/water Tomas bags. • Easty oanapmed. • Msaprom of some campounas. • Tectemelynot-m is <br /> • Selmpu • Bagstlenotngi fteteT6hounitoed. <br /> Soluble compounds and soil gas samples with lower concentrations of VOC wmpeunaa nava Lmlua hoaktq Wne as-3s be,n l« <br /> (i.e.,<0.1 pg/L or 100 pg/m). Samples with constituent concentrations lower beenshae'am be mon campemWsl. <br /> «°ble m <br /> than 0.l pglL and/or with polar/water soluble compounds should be confirmed sample:mlomemm° coca/«highly umitw volume can be anslVea N.5-5 N«recommtmdee. <br /> by Method TO-15. mslmn m by ming cosated al. sample collacuen <br /> IanJecuon leap aadh samples. N«whoa r«loxwosommW, raNNVoedoesn«campry <br /> samples. aft TO 15's <br /> 10. Other Modifications usedpamablecertas Idealre.nea Mayor be auto to l«nme Has earlems • conslderedmtean <br /> system(e.g..Harass) wrsening. typesorsamptltgmeNa.samples have 'supernatant-gas <br /> m bs mnsremetl I«analyns Ia.g., daomatogaph under <br /> Any other modifications not mentioned in this guidance should be reviewed by cants/«.o a e«rem«'ba section 1.e of m«hod. <br /> all parties involved prior to being put to use for project. The standard Nedmem,zone <br /> P e 9 P P J r msc Emiaommemal cbemNry Lob«stay/Ecu shoos be aonaueea <br /> operating procedures(SOP)for the sample preparation and analysis should <br /> 12110/2009 -75- 12/10/2009 _76- <br />
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