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2900 - Site Mitigation Program
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PR0508504
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Entry Properties
Last modified
2/14/2020 10:05:22 PM
Creation date
2/14/2020 2:51:33 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
COMPLIANCE INFO
RECORD_ID
PR0508504
PE
2950
FACILITY_ID
FA0008119
FACILITY_NAME
HOME DEPOT
STREET_NUMBER
0
Direction
W
STREET_NAME
GRANT LINE
STREET_TYPE
RD
City
TRACY
Zip
95376
CURRENT_STATUS
02
SITE_LOCATION
W GRANT LINE RD
P_LOCATION
03
P_DISTRICT
005
QC Status
Approved
Scanner
SJGOV\sballwahn
Tags
EHD - Public
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SECTION 3 <br /> SUBSURFACE EXPLORATION <br /> Subsurface exploration was conducted using a direct push drill rig to advance three borings to a <br /> maximum depth of 16 feet bgs each for sampling soil and groundwater. Further, composite <br /> samples of near surface soils were collected in three areas of the property. The approximate <br /> locations of the borings and composite sampling areas are shown in Figure 2. <br /> 3.1 FIELD METHODOLOGIES <br /> Field activities were conducted on 12 May, 1999. For evaluation of impacts from petroleum <br /> hydrocarbons, three direct push soil borings were completed to a depth of 16 feet below ground <br /> surface (bgs) by Precision Sampling of San Raphael, California under the supervision of <br /> WESTON. Soil was sampled continuously in a sampling tube fitted with acrylic liners. The <br /> borings were logged in accordance with the Unified Soil Classification System (USCS). Copies <br /> of the boring logs are included in Appendix A. Samples from the interval between 4.5 and 5 feet <br /> bgs were capped with teflon tape and plastic end caps, labeled, and then preserved in a cooler on <br /> ice for laboratory analysis. Soil samples from the borings were labeled according to the <br /> convention "SB-n-d," where "SB" signifies "soil boring," "n" refers to the boring number, and <br /> "d" indicates the approximate depth in feet bgs. <br /> A groundwater grab sample was collected from each boring upon removal of the soil <br /> probe/sampling tube. This was accomplished by inserting a temporary well screen and casing <br /> into the borehole and collecting a grab sample within the temporary well, using a new <br /> polyethylene disposable bailer. Groundwater samples were carefully poured from the bailer into <br /> appropriate sample containers, labeled, and then placed in a cooler on ice. Groundwater grab <br /> samples were labeled according to the convention "GW-n," where "GW" signifies <br /> "groundwater," and "n"refers to the boring number. <br /> For evaluation of potential impacts from pesticides and herbicides to surficial soil, composite soil <br /> samples were collected from three areas of the site. The locations of the three sample areas are <br /> shown in Figure 2. Eight discrete soil samples from the upper six inches of soil within each of <br /> the three composite sample areas were collected using a trowel. The eight discrete sample <br /> locations were dispersed randomly within each composite sampling area. Soil from the eight <br /> discrete samples was combined together and the resulting mixture was placed into glass sample <br /> jars. Each of the three composite sample containers were labeled and placed in a cooler on ice. <br /> The composite soil samples were labeled according to the convention "CP-n," where "CP" <br /> signifies "composite," and"n" refers to the area sampled. <br /> All sampling equipment was decontaminated between sample locations by washing with alconox <br /> detergent solution and rinsing with deionized water. The direct push borings were abandoned by <br /> filling with bentonite cement grout. Soil cuttings were transported off site and disposed of by <br /> Precision Drilling. <br /> S:\whc\wp\shared]\projects\homedepo\tracyph2.doe 3-1 July 1999 <br />
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