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ARCHIVED REPORTS_XR0010171
Environmental Health - Public
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3500 - Local Oversight Program
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PR0545689
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ARCHIVED REPORTS_XR0010171
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Last modified
5/18/2020 4:10:46 PM
Creation date
5/18/2020 3:37:38 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0010171
RECORD_ID
PR0545689
PE
3528
FACILITY_ID
FA0005164
FACILITY_NAME
FISCO WAREHOUSE
STREET_NUMBER
1648
STREET_NAME
SHAW
STREET_TYPE
RD
City
STOCKTON
Zip
00000
CURRENT_STATUS
02
SITE_LOCATION
1648 SHAW RD
P_LOCATION
01
P_DISTRICT
002
QC Status
Approved
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SJGOV\sballwahn
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EHD - Public
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I <br />' Site Background Information: Fisco Warehouse <br />' Page 5 of 6 <br /> eight-hour test. The flow rate was measured between 25 standard cubic feet per minute <br />' (scfm) and 30 scfm for the eight-hour test. Organic vapor (OV) readings ranged from <br /> 108 mg/kg to 363 mg/kg. Induced vacuum measured at the extraction well (VW-2) ranged <br /> from 54 inches to 72 inches of water. <br />' The greatest vacuum was measured in the observation point nearest the extraction well <br /> g <br /> (VW-1). The lowest vacuum was measured in MW-6, approximately 66 feet north of the <br /> extraction point. The maximum vacuum measured at the observation points during the pilot <br /> test was plotted versus the distance from the extraction well.The effective radius of Influence <br />' was determined by drawing a best-fit line though these data points to correlate distance to <br /> vacuum data. At a vacuum potential of 0.10 inches of water, the radius of influence is <br /> approximately 47 feet; at an induced vacuum potential of 1.0 inches of water, the radius of <br />' influence is approximately 30 feet; at 10.0 inches of water the radius of influence is <br /> approximately 13 feet.Based on the United States Environmental Protection Agency(EPA)- <br /> prepared document,How to Evaluate Alternative Cleanup Technologies For UST sites,the <br /> radius of influence is considered to be the distance from the extraction well at which a <br /> vacuum of at least 0.1 inches of water is observed.Based upon an effective vacuum potential <br /> of 0.1 inches of water, the calculated effective radius of influence at the site will be <br /> approximately 47 feet. <br /> On 31 July 2003, ground water monitoring well MW-8 was installed at the site to a depth of 95 feet <br /> bsg. Seven soil samples were submitted for laboratory analysis from pilot boring MW-8. THP-g, <br /> TPH-d,BTEX, and the five fuel additives were not detected at or above laboratory reporting limits <br /> in the soil samples submitted,nor were they detected at or above reporting limits in the first ground <br /> water sample collected from MW-8 in August 2003. <br /> SITE CONCEPTUAL MODEL <br /> Based on the data collected to date from soil borings and monitoring well installations, AGE has <br /> developed a site conceptual model for the release, migration and distribution of the contaminants in <br /> the subsurface as described below: <br /> The soil profile beneath the site is composed dominantly of sands and silts from surface grade to <br /> approximately 96 feet bsg,and finer-grained silts and clays from 96 feet bsg to total depth of 134 feet <br /> I bsg. <br /> Since initiation of ground water monitoring in February 2000,depth to ground water measurements <br /> I have fluctuated between a 33 feet btoc and 62 feet btoc. The inferred ground water flow direction <br /> generally has been towards the northwest (nine times) at gradients ranging between 0.001 ft/ft and <br /> . 0.008 ft/ft; ground water flow was towards the south four times at gradients between 0.01 ft/ft and <br /> Advanced GeoEnvironmental,Inc <br />
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