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2900 - Site Mitigation Program
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PR0521380
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Entry Properties
Last modified
3/5/2020 10:09:23 AM
Creation date
3/5/2020 9:49:14 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0521380
PE
2960
FACILITY_ID
FA0014524
FACILITY_NAME
TRACY TIRE
STREET_NUMBER
29425
Direction
S
STREET_NAME
MACARTHUR
STREET_TYPE
DR
City
TRACY
Zip
953779170
APN
25312026
CURRENT_STATUS
01
SITE_LOCATION
29425 S MACARTHUR DR
QC Status
Approved
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SJGOV\sballwahn
Tags
EHD - Public
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LFR Inc. <br /> • The annular space around the screened interval will be packed with sand/gravel to <br /> enable collection of representative groundwater samples. <br /> • The annular space above and below the screened interval will be appropriately <br /> sealed. <br /> • The well will be adequately developed. <br /> 3.4.1 Soil Boring Advancement <br /> The well will be installed by a C-57 licensed drilling contractor using a hollow-stem <br /> auger drill rig equipped with a split-spoon sampler. Soil samples will be collected for <br /> lithologic description at 10-foot intervals (at a minimum) during advancement of the <br /> soil boring. Soil lithology will be recorded in a lithologic log by a field geologist using <br /> the Unified Soil Classification System. The lithologic log will be prepared under the <br /> direct supervision of a California Professional Geologist who has expertise in <br /> stratigraphic well logging. The total depth of the boring will be determined in the field, <br /> based on the lithology encountered. Based on lithologic and groundwater elevation data <br /> collected from other wells at the Site, it is anticipated that the total depth of the boring <br /> will be approximately 125 feet bgs. <br /> 3.4.2 Monitoring Well Construction and Development <br /> After the boring has been advanced to the desired depth, the groundwater monitoring <br /> well will be constructed using flush-threaded, 2-inch-diameter, polyvinyl chloride <br /> (PVC) casing. The well screen will be 0.010-inch-slotted PVC casing. The length of <br /> the well screen will be based on the thickness of the water-yielding sediment <br /> encountered. Based on data collected from the five existing groundwater monitoring <br /> wells, it is anticipated that the screened interval will be approximately 20 feet long with <br /> approximately 5 feet above the groundwater table to accommodate seasonal <br /> fluctuations. Blank PVC casing will be installed from the top of the screened interval to <br /> the ground surface. Figure 4 presents a typical well construction diagram. <br /> After the well casing has been placed inside the augers, the well annulus materials <br /> (sand, bentonite, and grout) will be added. The well annulus opposite the screened <br /> interval will be filled with clean Number 2/12 Monterey sand to a height of <br /> approximately 3 feet above the top of the well screen. A minimum of 3 feet of <br /> bentonite chips will be placed and hydrated above the sand pack to isolate the screened <br /> interval from material above and prevent the entrance of grout into the sand pack. <br /> After the bentonite seal has hydrated, a clean cement-bentonite grout mix will then be <br /> placed in the annular space above the bentonite seal to the ground surface to seal the <br /> remainder of the borehole from the possible infiltration of surface water. <br /> The SJCEHD will be notified before the wells are sealed so that a field inspector may <br /> witness this activity. After the well is completed, the top of casing will be surveyed to <br /> the nearest 0.01 foot and tied into the elevations of the existing wells by a licensed <br /> surveyor. <br /> Page 4 wp�MW-08_Insta11-FebO6-fina1-M2506.d.:LFR <br />
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