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2900 - Site Mitigation Program
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PR0507920
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Last modified
5/17/2019 9:27:06 AM
Creation date
5/17/2019 9:23:58 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0507920
PE
2950
FACILITY_ID
FA0007836
FACILITY_NAME
SUNSTATE EQUIPMENT CO LLC
STREET_NUMBER
2000
Direction
W
STREET_NAME
CHARTER
STREET_TYPE
WAY
City
STOCKTON
Zip
95206
CURRENT_STATUS
02
SITE_LOCATION
2000 W CHARTER WAY
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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• Once driven into position, the disposable tip of the sampling device will be deployed by <br /> retracting the sampler rods approximately 4.5 feet, exposing the full screened interval. A 0.5- <br /> inch diameter, new disposable PVC bailer will then be used to withdraw the groundwater <br /> sample. <br /> • If the saturated zone is not encountered during the first HydropunchTM attempt, the sampling <br /> device will be removed from the borehole, and the borehole advanced to the total depth of the <br /> initial attempt. A second HydropunchTM attempt will then be made. This process will be <br /> repeated until the saturated zone is encountered, and a groundwater sample is collected. <br /> • Once collected, samples will be placed in laboratory-prepared sample containers in order of <br /> the volatility of the target analytes. Samples will be decanted from the bailer into the sample . <br /> containers with minimal sample agitation and aeration. For volatile organic compounds <br /> (VOCs), the sample containers will consist of 40-m1 glass vials with Teflon""-lined septa, and <br /> containing dilute (50%) hydrochloric acid as a preservative. During containerization of the <br /> VOC samples, the 40-m1 glass vials will be filled to slightly overflowing, forming a meniscus <br /> at the opening of the container. The cap will then be secured to the top of the vial. The vial <br /> will be inverted and gently tapped and examined for the presence of bubbles. If air bubbles <br /> are observed in the vial, additional sample is added to the vial. If air bubbles are still present <br /> in the vial, the sample will be discarded and a new vial will be utilized. <br /> • Groundwater samples will be labeled with a distinct identification number, the date and time <br /> of collection, the sampler's initials, any sample preservatives, and the desired analyses. <br /> Sample bottles will also be secured with a custody seal which will overlap the cap and will be <br /> labeled with the same information. <br /> • Once collected and prepared, samples will either be immediately delivered to a mobile <br /> laboratory for on-site analysis, or placed in a cooler with ice for delivery to a fixed-base <br /> laboratory for analysis. A chain-of-custody form will accompany the samples at all times and <br /> will include the site location, the project number, name of sampler, sample numbers, dates and <br /> times of collection, number of containers, and analyses requested. <br /> • Following completion of the groundwater sampling, the soil borings will be filled with a <br /> cement grout mixture to the ground surface in accordance with ADWR R12-15-816. The <br /> grout will be allowed to settle and set up, and then the soil boring will be refilled with grout. <br /> The surface pavement will be patched (if required) with similar materials (asphalt cold patch <br /> for asphalt pavement and concrete for concrete slabs or pavement). <br /> • Any excess water from the HydropunchTM sampling will be stored in 55-gallon drums or <br /> storage tanks pending characterization and disposal. Small quantities of wat 1� <br /> with the decontamination fluids. <br /> 11g� <br /> APR 16 1998 <br /> ® ENVIRONMENTAL HEALTH <br /> GEC Standard Operating Procedure PERMIUSERVICES <br /> Last Revision December 1997 2 <br />
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