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ARCHIVED REPORTS_XR0008817
Environmental Health - Public
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26 (STATE ROUTE 26)
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8203
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3500 - Local Oversight Program
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PR0545707
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ARCHIVED REPORTS_XR0008817
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Last modified
11/20/2024 8:48:27 AM
Creation date
5/13/2020 4:01:16 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0008817
RECORD_ID
PR0545707
PE
3528
FACILITY_ID
FA0003591
FACILITY_NAME
JOHN M RISHWAIN
STREET_NUMBER
8203
Direction
E
STREET_NAME
STATE ROUTE 26
City
STOCKTON
Zip
95215-9536
APN
10114021
CURRENT_STATUS
02
SITE_LOCATION
8203 E HWY 26
P_LOCATION
99
P_DISTRICT
002
QC Status
Approved
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EHD - Public
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02 June 2004 <br /> AGE-NC Project No 99-0645 <br /> Page 5 of 5 <br /> SITE CONCEPTUAL CONCLUSIONS <br /> Based on the data collected from the site, AGE concludes <br /> ■ The sand units occurred at depths of 15 to 30 feet bsg and 75 or 80 feet to 80 or 85 feet bsg <br /> The deepest sand unit previously encountered may actually be two thinner units Groundwater <br /> was encountered at approximately 96 feet bsg Ground water flow direction at the site was <br /> northwest The decrease of ground water elevation of approximately 4 feet between July 2002 <br /> and October 2003 may be due to seasonal fluctuation <br /> • TPH-g was detected in the soil boring sample collected north of the site (B6') Low <br /> concentrations of MTBE were detected in the soil sample to a depth of 55 feet bsg in the same <br /> boring Benzene concentrations were detected in the two deepest soil samples collected from <br /> the northern boring, indicating the northern migration of only benzene, at a depth of 60 feet <br /> to 70 feet bsg or the presence of another source off the northern edge of the site With no <br /> detections of benzene in the upper 55 feet of boring B676, only low detections of benzene in <br /> the former UST soil boring 131, all less than 0 1 mg/kg, and the lack of detectable <br /> hydrocarbons in the soil boring MW-1R below 50 feet bsg, the source of the off-site benzene <br /> detected in the further most reach of boring B6' appears to be from another source than the <br /> UST release However, soil vapor extraction on the site will likely effectively mitigate the <br /> . detections off-site <br /> TPH-g was not detected in the soil boring sample collected at the west edge of the site(VW3) <br /> Only low concentrations of MTBE were detected at 30 and 40 feet bsg in boring VW3 TPH-g <br /> was not detected in the soil boring sample collected at the southern edge of the site(B7) Only <br /> one detection of MTBE was in the soil, from 30 feet bsg in boring B7 <br /> TPH-g was only detected in the upper most soil sample from boring VW1A, at the east edge <br /> of the site MTBE was detected in samples from boring B7 from 40 feet to 60 feet bsg The <br /> lateral extent of adsorbed MTBE may extend below the eastern boundary of the site Soil vapor <br /> extraction on the site will likely effectively mitigate the MTBE off-site <br /> • Generally, the highest concentrations of MTBE were detected within a 45 foot thick interval, <br /> generally occurring between 15 feet and 60 feet The vertical extent of the MTBE-impacted <br /> soil was limited to less than 70 feet bsg <br /> • MTBE was detected in one ground water sample(MW-1) at a concentration of 120 µg/1 This <br /> concentration does exceed the maximum contaminant level for MTBE in drinking water <br /> • Based upon effective vacuum potential of 0 1 inches of water, the calculated effective radius <br /> of influence at the site for vapor wells screened from 15 feet to 40 feet bsg will be <br /> approximately 40 feet The calculated effective radius of influence at the site for vapor wells <br /> screened from 40 feet to 70 feet bsg or greater will be approximately 30 feet <br /> • TPH-g,TPH-d and BTEX compounds were not detected in the three water samples collected <br /> • Advanced GeoEnvsronmenW <br />
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