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2900 - Site Mitigation Program
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PR0526755
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Last modified
2/11/2019 4:19:41 PM
Creation date
2/11/2019 3:39:55 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0526755
PE
2950
FACILITY_ID
FA0018115
FACILITY_NAME
BROOKSIDE ASSOCIATION
STREET_NUMBER
6331
STREET_NAME
BROOK HOLLOW
STREET_TYPE
CIR
City
STOCKTON
Zip
95219
APN
11637026
CURRENT_STATUS
01
SITE_LOCATION
6331 BROOK HOLLOW CIR
P_LOCATION
01
P_DISTRICT
003
QC Status
Approved
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EHD - Public
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1 0 .0 <br /> Field Investigation Work Plan <br /> Brookside Estates,Stockton, California 1/9/07 Sert Consulting,Inc. <br /> ' <br /> All drilling locations will be backfilled with a cement/bentonite grout immediately after sampling. <br /> 2.2 Soil Sampling <br /> Soil samples from the borings will be submitted for soil property analysis as determined by SERT. <br /> Samples from direct-push borings will be collected by extracting the acetate or brass liner from within the <br /> drive rod at the desired depth. Liners will be 0.5 feet in length. Upon retrieval,the ends of the sample <br /> liners will be sealed with plastic end caps and wrapped with duct tape to hold the soil within the liners and <br /> maintain soil moisture content during shipment to the testing laboratory. <br /> 2.3 Grab Groundwater Sampling <br /> ' Four temporary borings will be used as grab groundwater sampling locations. These will not be <br /> constructed as typical monitoring wells. After reaching approximately three feet below the water line,the <br /> drive rods will be retracted several feet to allow groundwater to enter the boring for a grab groundwater <br /> sample with a disposable bailer. Water sampling will be performed through the drilling rods or augers to <br /> maintain the hole during water sampling. An inner exposed screen is preferred for sampling, similar to <br /> Hydropunch or Geoprobe methods. A diagram of a typical boring and the anticipated abandonment <br /> method is presented in Figure 6. <br /> 2.4 Groundwater Sampling Methods <br /> ' Groundwater samples will be collected from the temporary borings using a HydroPunch sampling tool or <br /> equivalent. Once the targeted sampling depth is reached,the HydroPunch tool will be pushed several feet <br /> into the saturated formation. The drive pipe will be pulled upward to open the inlet of the sampler, <br /> allowing groundwater to flow into the screened sample chamber. Purging or well development will not <br /> be required. Samples will be collected from the sample chamber using a stainless steel or disposable <br /> bottom-emptying bailer. Samples to be submitted for metals will be filtered during collection with a <br /> 0.45-micron in-line filter prior to delivery to the lab. <br /> 2.5 Water Level Measurements <br /> During groundwater sampling in the four locations,the depth to water will be measured with a water level <br /> sounder for future reference. <br /> 2.6 Field Quality Control Measures <br /> Quality control measures will be implemented for all field work to maintain the quality and reliability of <br /> the collected data. For water sampling, one duplicate sample will be collected and tested for similar <br /> parameters along with the four planned water samples. Details of additional quality control measures that <br /> will be implemented are described in Section 3. <br /> 2.7 Equipment Decontamination <br /> rAll down-hole equipment that comes into contact with groundwater will be cleaned before and after use, <br /> and/or between uses at different sampling locations. Cleaning consists of washing using a phosphate-free <br /> detergent wash followed by a deionized or distilled water rinse. <br /> g <br /> 2.8 <br /> Investigation Derived Waste <br /> Soil cuttings will be kept to a minimum by using small diameter hollow stem augers or the direct-push <br /> drilling method. Only discarded soils from the sampling efforts will require disposal. Since there are no <br /> r 3 <br />
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