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WORK PLANS 1994-2010
Environmental Health - Public
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EHD Program Facility Records by Street Name
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2900 - Site Mitigation Program
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PR0540667
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WORK PLANS 1994-2010
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Last modified
2/8/2019 8:42:54 AM
Creation date
2/7/2019 4:39:15 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
FileName_PostFix
1994-2010
RECORD_ID
PR0540667
PE
2960
FACILITY_ID
FA0023252
FACILITY_NAME
WELDON CHURCH PROPERTY
STREET_NUMBER
104
Direction
W
STREET_NAME
BEVERLY
STREET_TYPE
PL
City
TRACY
Zip
95376
CURRENT_STATUS
01
SITE_LOCATION
104 W BEVERLY PL
QC Status
Approved
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WNg
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EHD - Public
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.Ol <br /> 12 February 1996 <br /> AGE-NC Project No.95-0106 <br /> Page 3 of 6 <br /> ground water monitoring wells: one monitoring well will be located in vicinity of probing six (P6); <br /> a second well will be located south of probing two (P2) on the adjacent property (also owned by <br /> Weldon Church); a third well will be placed in the City of Tracy right of way east of the driveway; <br /> and a fourth well will be located in the City of Tracy right-of-way along the north side of Beverly <br /> Place. Proposed monitoring well locations are illustrated in Figure 2. <br /> Each well should be designed with four-inch casings screened from 3 to 15 feet in depth, this will <br /> allow for adequate ground water recharge during sampling. Monitoring well design is illustrated in <br /> Figure 3 -Xfonitoring Well Design. <br /> Each boring will be advanced utilizing a truck-mounted, hollow stem drill rig equipped with 8.25-inch <br /> hollow-stem augers. Soil samples will be collected beginning at a depth of 3 feet bsg. Samples will <br /> be collected using a California split-spoon sampler and brass sleeves or a continuous core sampler. <br /> The samples will be driven by dropping a 140-pound weight fi-om a height of 30 inches. The number <br /> of blows required to drive each 6-inch length of the sampler blow counts) are to be recorded on the <br /> boring logs by an AGE staff geologist. <br /> Upon sample retrieval, the middle brass sleeve will be removed from the sampler. The ends of the <br /> sleeve will be inunediately covered with Teflon sheets, sealed with plastic end caps, secured with tape <br /> and immediately placed under ice in a chilled container for transportation to a State-certified <br /> laboratory. Each soil sample sleeve will be labeled with the following: boring location, vertical depth, <br /> time, date and sampler's initials. <br /> 3.2. EQUIPMENT DECONTAXIINATION <br /> Ail 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 stein augers are steam-cleaned prior to <br /> advancement in each borehole. <br /> 3.3. LABORATORY ANALYSIS <br /> Selected soil and ground water samples will be analyzed for TPH-g, BTE&X, methyl-tert-butyl ether <br /> (MTBE) and total organic carbon(TOC) in accordance with EPA methods 8015m/5030, 8020/602, <br /> 8020/602 and 9060, respectively. Laboratory reports of both soil and ground water analyses, testing <br /> methods, laboratory quality assurance/quality control (QA/QC) reports, and sample chain of custody <br /> documentation will be presented in a report with the findings and recommendations. <br /> Duplicate soil samples may be released to a State-certified laboratory to be analyzed for intrinsic <br /> permeability, moisture content and porosity in accordance with the appropriate ASTM methods. <br />
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