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2900 - Site Mitigation Program
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PR0523858
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Last modified
1/14/2020 4:20:56 PM
Creation date
1/14/2020 3:34:04 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0523858
PE
2960
FACILITY_ID
FA0016067
FACILITY_NAME
FORMER BUFFALO TANK
STREET_NUMBER
5709
Direction
E
STREET_NAME
FREMONT
STREET_TYPE
ST
City
STOCKTON
Zip
95205
APN
10123019
CURRENT_STATUS
01
SITE_LOCATION
5709 E FREMONT ST
P_LOCATION
99
P_DISTRICT
002
QC Status
Approved
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06 January 2003 <br /> AGE-NC Project No. 02-0896 <br /> Page 6 of 7 <br /> sampling and well installation, the augers remain in the ground, thus providing stability to the <br /> borehole. <br /> Sampling of the boring will be conducted through the hollow stem of the augers. Relatively <br /> undisturbed soil samples will be collected using a California Modified split-spoon sampler loaded <br /> with three 2-inch by 6-inch brass sleeves. The sampler will be driven by dropping a 140-pound <br /> hammer from a height of 30 inches. The sampler will be driven 18-inches or until refusal into the <br /> undisturbed soil below the bit on the lead auger. <br /> Upon removal from the sampler,the sample sleeves will be separated using a clean knife. Based on <br /> the amount of sample recovery, either of the leading sample sleeves will be preserved for possible <br /> laboratory analysis by covering the exposed ends of the sleeve with Teflon sheets,plastic end caps <br /> and sealed with tape. <br /> Following sample collection, each preserved sample sleeve apA will be labeled with the boring <br /> location, depth, time, date and sampler's initials. Appropriately sealed and labeled samples will be <br /> placed in a chilled container under ice and will be transported under chain-of-custody procedure to <br /> a DHS-certified laboratory. <br /> Soil encountered in the borings will be visually classified by an AGE geologist or environmental <br /> specialist in accordance with the Unified Soil Classification System (USCS). Additionally, soil <br /> samples will be field-screened for the presence of volatile organic compounds using an OVM. <br /> Investigation-derived waste,including soil cuttings and decontamination rinseate,generated during <br /> drilling activities will be containerized in appropriately labeled DOT-approved 55-gallon drums and <br /> stored on-site pending disposal. Appropriate disposal alternatives will be determined based on <br /> laboratory results of soil and water analysis. <br /> 4.2. GRAB GROUND WATER SAMPLING PROCEDURES <br /> The soil boring will be advanced to the top of the ground water table, as identified by collection of <br /> a saturated soil sample, to collect a grab ground water sample. Once ground water has been <br /> encountered, a hydropunch-equivalent water sampling device will be driven two to three feet into <br /> the water-bearing zone.Ground water samples will be collected with a hydropunch-equivalent water <br /> sampling assembly fitted with one-inch diameter 0.010-inch slotted temporary well screen. Each <br /> ground water sample will be extracted by lowering a bailer through the hollow center of the drive <br /> rods and into the screen section.Depending on subsurface and drilling conditions,grab ground water <br /> samples may also be collected directly through the hollow stem augers using a new disposable bailer. <br /> Advanced GeoEnvironmental,Inc. <br />
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