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Environmental Health - Public
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EHD Program Facility Records by Street Name
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99 (STATE ROUTE 99)
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2900 - Site Mitigation Program
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PR0522133
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COMPLIANCE INFO
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Last modified
11/19/2024 1:56:07 PM
Creation date
5/1/2020 8:56:24 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
COMPLIANCE INFO
RECORD_ID
PR0522133
PE
2950
FACILITY_ID
FA0015088
FACILITY_NAME
DEL VALLE HOMES
STREET_NUMBER
3995
Direction
S
STREET_NAME
STATE ROUTE 99
City
STOCKTON
Zip
952158027
APN
17918025
CURRENT_STATUS
01
SITE_LOCATION
3995 S HWY 99
QC Status
Approved
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SJGOV\sballwahn
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EHD - Public
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Geolog&Ot7CChXtcslac. Pa-e 2 <br /> Soil Investigation Work Plan <br /> Project No. 1117.2 <br /> November 12,2003 <br /> 2.1 Tank Location Search <br /> GTI has researched the EHD and County Accessor files to determine the actual site of the <br /> former UST. Included in these files are Aerial photos, Tentative Subdivision Map of Little <br /> John Creek, and previous facility maps. The location of the former tank has been plotted on <br /> Figure 3A & 3B — Sample Points for this work plan. Using wooden stakes the location of <br /> the boreholes will be mark on the ground. <br /> 2.2 Borehole Drilling& Soil Sample Collection <br /> Two boreholes will be drilled in the area described above as the location of the former UST. <br /> These boreholes will be drilled using a GeoProbe rig owned and operated by V&W Drilling <br /> of Isleton, CA (C574 720904). <br /> The GeoProbe advances a coring tool with a pneumatic hammer to a selected depth. Upon <br /> reaching that depth, a coring tool is opened and advanced further to fill the core barrel. The <br /> soil sample enters an acetate cylinder contained in the coring tool. Upon filling, the coring <br /> tool is pulled from the hole and the cylinder is removed. The cylinder is then cut and the <br /> selected interval is capped with plastic end caps and placed on ice for shipment to the <br /> laboratory. The remainder is used for geologic logging. <br /> A boring log providing sediment description using the USCS and other field observations as <br /> described below will be maintained by a professional geologist working under the <br /> supervision of a registered geologist. Two soil samples from each borehole will be <br /> submitted to the laboratory for analysis. One of these soil samples will be collected from <br /> fifteen feet and one from twenty feet below existing grade. <br /> Since only selected soil samples collected will be submitted for laboratory analysis, a <br /> screening process will be used to gather additional information through field observation. <br /> These observations will include: <br /> • Sediment type, especially grain size and clay content <br /> • Moisture content <br /> • Visible evidence of contamination, i.e., color change due to reduction of iron or <br /> discoloration from hydrocarbons and other pollutants <br /> • Readings above background on an organic vapor meter(OVM) <br /> The OVM is a portable photo ionization detector that uses a 10.6 eV lamp to detect <br /> compounds with ionization potential below 10.6 eV (hydrocarbon range). <br /> 2.3 Soil Laboratory Analyses <br /> Two soil samples from each GeoProbe borehole will be submitted to Sherwood <br /> Laboratories of Hilmar(State Certified Laboratory#1400) for the following analysis: <br /> • Oxygenates (5)by EPA method 8260 <br /> A Chain of Custody will be completed for all samples collected and tracked to ensure <br /> sample integrity. The detection limits for these compounds are listed below. <br /> DetectionLimits: Oxygenates <br /> Soil (Ag/Kg) <br />
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