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2900 - Site Mitigation Program
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PR0522629
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Last modified
2/15/2019 10:54:59 AM
Creation date
2/15/2019 10:19:41 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0522629
PE
2950
FACILITY_ID
FA0015420
FACILITY_NAME
CALIFORNIA STREET MEDICAL BLDG
STREET_NUMBER
1617
Direction
N
STREET_NAME
CALIFORNIA
STREET_TYPE
ST
City
STOCKTON
Zip
95204
APN
12715050
CURRENT_STATUS
02
SITE_LOCATION
1617 N CALIFORNIA ST
P_LOCATION
01
P_DISTRICT
002
QC Status
Approved
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EHD - Public
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11 August 2004 <br /> AGE-NC Project No. 04-1180 <br /> Page 5 of 8- <br /> 4.1. SOIL BORINGS <br /> The soil boring will be advanced utilizing a truck-mounted Hollow-stem-drill rig with 8.25-inch <br /> diameter hollow-stem augers. The proposed soil boring .location is illustrated in Figure 2. Soil <br /> samples will be collected at five-foot intervals beginning at 5 feet bsg to total depth. Relatively <br /> undisturbed soil samples will be collected in each of the borings utilizing a California modified split- <br /> spoon sampler fitted with 2-inch diameter, 6-inch long brass sleeves. Upon removal from the <br /> sampler, the sample sleeves will be separated with a knife. The exposed ends of the second sleeve <br /> will be covered with Teflon sheets, capped and sealed with tape. Soils sampled in the borings will <br /> be visually classified by an AGE geologist in accordance with the Unified Soil Classification System <br /> (USCS). Additionally, soil samples will be field screened for the presence of volatile organic <br /> compounds using an organic vapor meter(OVM),equipped with a photo ionization detector(PID). <br /> Soil sample descriptions and OVM readings will be recorded on a log for each boring. <br /> Following sample collection,each preserved sample sleeve will be labeled with the boring location, <br /> depth,time, date and sampler's initials. Appropriately sealed and labeled samples will be placed in <br /> a chilled container under ice and transported under-chain of custody procedure to a DHS-certified <br /> laboratory. <br /> 4.2. WELL.COMPLETION <br /> The ground water monitoring wells will be completed utilizing 1-inch diameter schedule 40 . <br /> polyvinylchloride.(PVC) 0.010-inch slotted well screen and blank well casing. A 20-foot length of <br /> well screen is anticipated for installation ofthemonitoring well. <br /> After installing the well casing in each pilot boring, a filter pack material consisting of pre-washed <br /> #2/12 Lonestar sand will be added through the augers over the screen interval to approximately two <br /> feet above the screened interval. Following placement of the filter pack, the well will be surged to <br /> assist in settling the filter pack. Additional sand will be added.if settling occurs. <br /> A nominal two-foot bentonite seal (pell plug non-coated bentonite chips)will be placed above the <br /> filter pack to minimize the potential for grout penetration into the screened section of the well. The <br /> bentonite seal will be formed by pouring bentonite chips into the annulus and allowing them to settle <br /> on the filter pack. The bentonite pellets will be allowed to hydrate for a minimum of one-half hour <br /> prior to grouting. <br /> The remaining annular space will be filled within one foot of the ground surface with a cement grout. <br /> The grout mixture will consist of Type PH portland neat cement and not more than 6 gallons of water <br /> per 94-pound sack of cement. The grout will be placed by pumping through tremie pipe. <br /> Advanced GeoEnvironmental,Inc. <br />
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