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2900 - Site Mitigation Program
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PR0517512
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Entry Properties
Last modified
11/1/2018 8:52:12 PM
Creation date
11/1/2018 3:15:20 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0517512
PE
2960
FACILITY_ID
FA0013476
FACILITY_NAME
FTG CONSTRUCTION MATERIALS, INC
STREET_NUMBER
925
Direction
W
STREET_NAME
ANDERSON
STREET_TYPE
ST
City
STOCKTON
Zip
95202
CURRENT_STATUS
01
SITE_LOCATION
925 W ANDERSON ST
P_LOCATION
01
QC Status
Approved
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EHD - Public
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Mr. Ross Atkinson <br />Page 2 of 4 <br />published information (San Joaquin County Flood Control & Water Conservation District) <br />groundwater is expected to flow toward the east or northeast. <br />Analytical Results of Broken Tile Material <br />On August 23, 2001, Advanced GeoEnvironmental collected twenty samples of the tile material. <br />Laboratory analysis detected concentrations of total TPHd ranging from 200 to 2,500 parts per <br />million (ppm) and averaging 1,010 ppm. Leachable concentrations of TPHd (DI -WET extraction) <br />ranged from 11 ppm to 38 ppm and averaged 22 ppm. Leachable Cr6 ranged from 10 parts per <br />billion (ppb) to 40 ppb and averaged 26.5 ppb. <br />PROPOSED SCOPE OF INVESTIGATION <br />To investigate whether the contaminants have impacted groundwater, Ground Zero proposes to drill <br />and sample three soil borings at the approximate locations shown on Figure 2. Based upon the data <br />obtained, groundwater monitoring wells may or may not be proposed. <br />Drilling and Discrete Soil and Groundwater Sampling <br />Drilling will be conducted under the supervision of an experienced geologist. A C-57 licensed <br />drilling contractor will advance the soil borings using a Geoprobe rig. Soil will be classified in <br />accordance with ASTM Designation D2488-90, which is equivalent to the Unified Soil <br />Classification System. A photoionization detector (PID) will be used to screen all soil samples for <br />evidence of hydrocarbon contamination. Soil and groundwater samples will be collected from the <br />borings for laboratory analysis. <br />Direct Push Drilling and Sample Collection <br />A total of three soil borings will be advanced at the approximate locations shown on Figure 2 using a <br />truck mounted Geoprobe rig. One boring will be placed in the indicated downgradient direction of the <br />tile stockpile. One boring will be located immediately upgradient of the stockpile and the third boring <br />will be located near the extreme southwestern comer of the property. This boring is intended to serve <br />as a background sampling point. The borings will be drilled to fust groundwater, which is expected to <br />occur at a depth of 30 feet or less. Upon completion, the soil borings will be backfilled with neat <br />cement grout to ground surface. <br />Soil samples will be collected from the borings at five-foot intervals to total depth for lithologic <br />identification and field screening for contamination. Selected soil samples will be submitted to a <br />State -certified laboratory for analysis. Soil sample selection will be based on field evidence of <br />petroleum hydrocarbon contamination such as discoloration, odors, PID readings, as well as <br />lithologic changes. If no evidence of contamination is noted in the field, two soil samples from <br />each boring will be selected for analysis based on lithology. Samples selected for analysis will be <br />immediately capped, segregated and preserved by placing in an ice chest at a temperature of <br />approximately 4°C, and wil be transported to the laboratory under chain of custody protocol. <br />G:\GROUNDZE\Alcgm\REPOItTS\hydpuWKPLAN.doc <br />
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