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ARCHIVED REPORTS_XR0002146
Environmental Health - Public
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3500 - Local Oversight Program
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PR0545213
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ARCHIVED REPORTS_XR0002146
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Last modified
1/27/2020 5:07:57 PM
Creation date
1/27/2020 4:51:13 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0002146
RECORD_ID
PR0545213
PE
3528
FACILITY_ID
FA0005338
FACILITY_NAME
J B TERMINAL CO
STREET_NUMBER
6700
STREET_NAME
GRANT LINE
STREET_TYPE
RD
City
TRACY
Zip
95376
CURRENT_STATUS
02
SITE_LOCATION
6700 GRANT LINE RD
P_LOCATION
03
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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k-acing volume Once the well is purged .and inJ1C,3tnr <br /> parameters have stabilized, a sample will be collected after <br /> the water level approaches 80 percent of i t s 1.11 4 t i-a 1 <br /> elevation. Where water level recovery is slow , t1le sample <br /> will be collected after stabilization is achieved and enough <br /> water is present to fill sample containers . <br /> Cross contam.Lnat:ion from transferring pumps ( or bailers ) <br /> from well to well will be avoided by utilizing dedicated <br /> equipment. Where this is not feasible, thorough cleaning of <br /> equipment will br: performed between sampling rounds . <br /> Sampling will proceed from the least contaminated to the <br /> most contaminated well, if information is available before <br /> sample collection, or if it is indicated by field evidence. <br /> Where several types of analysis will be performed for a <br /> given well, individual samples will be collected in the <br /> following order: <br /> 1. Volatile organics <br /> 2. Purgeable organic carbon <br /> 3. Purgeable organic halogens <br /> 4. Total organic carbon <br /> 5. Total organic halogens <br /> 6 . Extractable organics <br /> 7 . Total metals <br /> 8. Dissolver) metals <br /> g. Phenols <br /> 10. Cyanide <br /> The specific analytical methods be utilized for the common <br /> volatile/semivolatile to analyses are shown on Table 2. <br /> i <br /> Groundwater samples will be collected with a teflon bailer <br /> with bottom emptying device. Duplicate samples will be <br /> transferred to vials or containers that meet Regional Board <br /> sper-i,fications (Table l ) . Groundwater from the bailer will <br /> be transferred to the sample container by allowing the fluid <br /> to flow slowly along the sides of the vessel All <br /> containers will be filled above the top of the opening to <br /> form a positive meniscus. No head space should be present <br /> in the sample container once it as sealed_ After the vial is <br /> capped it will be inverted to check for air bubbles . if <br /> bubbles are present the sample will be discarded and <br /> replaced. if it is not possible to collect a sample without <br /> head space, the problem will be notea on the f teld <br /> technician' s sampling log. <br /> Immediately following sample collection, samples will be <br /> labeled and stored in an ice chest containing frozen <br /> chemical ice sealed in plastic bags. Sample labels —L11 <br /> contain the following information: dat -, time, project ID, <br /> sample ID, name of sampler and type of analysis . All <br /> samples gill. be transported under chain-of-custody protocol <br /> to a state certified laboratory within 24 hours. A sample <br /> container filled in tt,e l.akoratcry with organic free w.-ter <br />
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