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2900 - Site Mitigation Program
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PR0515525
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Entry Properties
Last modified
10/24/2018 4:25:05 PM
Creation date
10/24/2018 1:36:37 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0515525
PE
2950
FACILITY_ID
FA0012215
FACILITY_NAME
RCCI PTP
STREET_NUMBER
14253
Direction
S
STREET_NAME
AIRPORT
STREET_TYPE
WAY
City
MANTECA
Zip
95336
APN
19803031
CURRENT_STATUS
01
SITE_LOCATION
14253 S AIRPORT WAY
P_LOCATION
04
P_DISTRICT
003
QC Status
Approved
Scanner
WNg
Tags
EHD - Public
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CRA <br /> Field Screening <br /> One of the remaining tubes is partially emptied leaving about one-third of the soil in the tube. The tube is <br /> capped with plastic end caps and set aside to allow hydrocarbons to volatilize from the soil. After ten to <br /> fifteen minutes, a portable photoionization detector (PID) measures volatile hydrocarbon vapor <br /> concentrations in the tube headspace, extracting the vapor through a slit in the cap. PID measurements are <br /> used along with the field observations, odors, stratigraphy and ground water depth to select soil samples <br /> for analysis. <br /> Water Sampling <br /> Water samples, if they are collected from the boring, are either collected using a driven Hydropunch type <br /> sampler or are collected from the open borehole using bailers. The ground water samples are decanted into <br /> the appropriate containers supplied by the analytic laboratory. Samples are labeled, placed in protective <br /> foam sleeves, stored on crushed ice at or below 4°C, and transported under chain-of-custody to the <br /> laboratory. <br /> Duplicates and Blanks <br /> Blind duplicate water samples are collected usually collected only for monitoring well sampling programs, <br /> at a rate of one blind sample for every 10 wells sampled. Laboratory-supplied trip blanks accompany <br /> samples collected for all sampling programs to check for cross-contamination caused by sample handling <br /> and transport. These trip blanks are analyzed if the internal laboratory QA/QC blanks contain the <br /> suspected field contaminants. An equipment blank may also be analyzed if non-dedicated sampling <br /> equipment is used. <br /> Grouting <br /> If the borings are not completed as wells, the borings are filled to the ground surface with cement grout <br /> poured or pumped through a tremie pipe. <br /> Waste Handling and Disposal <br /> Soil cuttings from drilling activities are usually stockpiled onsite on top of and covered by plastic sheeting. <br /> At least four individual soil samples are collected from the stockpiles for later compositing at the analytic <br /> laboratory. The composite sample is analyzed for the same constituents analyzed in the borehole samples. <br /> Soil cuttings are transported by licensed waste haulers and disposed in secure, licensed facilities based on <br /> the composite analytic results. <br /> Ground water removed during sampling and/or rinsate generated during decontamination procedures are <br /> stored onsite in sealed 55 gallon drums. Each drum is labeled with the drum number, date of generation, <br /> suspected contents, generator identification and consultant contact. Disposal of the water is based on the <br /> analytic results for the well samples. The water is either pumped out using a vacuum truck for transport to <br /> a licensed waste treatment/disposal facility or the individual drums are picked up and transported to the <br /> waste facility where the drum contents are removed and appropriately disposed. <br /> F:\TEMPLATEMPsToring.doc <br /> 2 of 2 <br />
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