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2900 - Site Mitigation Program
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PR0541653
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Last modified
7/8/2020 3:40:25 PM
Creation date
7/8/2020 3:38:30 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0541653
PE
2965
FACILITY_ID
FA0023871
FACILITY_NAME
TOP FILLING STATION
STREET_NUMBER
101
Direction
S
STREET_NAME
WILSON
STREET_TYPE
WAY
City
STOCKTON
Zip
95205
APN
15125307
CURRENT_STATUS
01
SITE_LOCATION
101 S WILSON WAY
P_LOCATION
01
QC Status
Approved
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EHD - Public
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O8 July 1999 <br /> AGE-NC Project No. 95-0130 <br /> Page 8 of 10 <br /> 8-inch diameter hollow-stem augers. Cuttings generated during drilling activities will be placed on <br /> plastic sheeting and covered. Rinseate will be containerized in properly labeled D.O.T. 55-gallon <br /> drums, and stored on-site in an area lacking public access. Disposal alternatives will be evaluated <br /> based on results of soil and water analysis. <br /> Soil samples will not be collected from replacement wells located near MW-I through MW-5; <br /> however,soil samples will be collected at five-foot intervals beginning at a depth of 15 feet bsg from <br /> all other proposed downgradient wells. Soil samples will be collected utilizing a California split- <br /> spoon sampler and brass sleeves. The sampler will be driven by dropping a 140-pound weight from <br /> a height of 30 inches (blow counts) and record the number of blow counts on the boring logs. Upon <br /> soil sample retrieval, the middle brass sleeve will be removed from the sampler. The ends of the <br /> brass sleeve will be immediately covered with Teflon or aluminum sheets, sealed with plastic end <br /> caps, secured with tape and immediately placed in a chilled container for storage pending <br /> transportation to a state-certified laboratory. Each sample sleeve will be labeled with the following: <br /> boring location, depth, time, date and sampler's initials. <br /> During sampling activities, sample duplicates will be monitored for the presence of organic vapor <br /> using a photo-ionization detector (PID: Thermo Environmental 580A, 10.0 eV, calibrated to <br /> isobutylene) and will be described on boring logs using the Unified Soil Classification System <br /> (USCS). <br /> All sampling tools and brass sleeves used for sample collection will be thoroughly rinsed with clean <br /> water after washing with a solution of Alconox. All hollow stem augers will be steam-cleaned prior <br /> to advancement in each borehole. <br /> 4.3. MONITORING WELL COMPLETION <br /> Following completion of monitoring well drilling, a 2-inch diameter, Schedule 40 PVC 0.020-inch <br /> slotted well screen and casing will be installed. Based on the depth of the boring and ground water <br /> table,a 20-foot length of well screen will be installed. It is anticipated that the well section will be <br /> placed across the top of the saturated zone with a portion of the well screen section extending five <br /> feet above the water table. <br /> After installing the well casing,filter pack material consisting of pre-washed#3 Lonestar sand will <br /> be added from the bottom of the borehole to approximately two feet above the screened interval. <br /> Following placement of the filter pack, the well will be surged to assist in settling the filter pack. <br /> Additional sand will be added if settling occurs. <br /> A nominal two-foot bentonite seal (bentonite chips) will be placed above the filter pack to minimize <br /> Advanced GeoEnvironmental,Inc. <br />
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