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ARCHIVED REPORTS_XR0005940
EnvironmentalHealth
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2900 - Site Mitigation Program
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PR0534875
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ARCHIVED REPORTS_XR0005940
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Last modified
4/7/2020 2:08:28 PM
Creation date
4/7/2020 1:46:54 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0005940
RECORD_ID
PR0534875
PE
2960
FACILITY_ID
FA0020170
FACILITY_NAME
AAA TRUCK WASH/JIMCO TRUCK PLAZA
STREET_NUMBER
1022
Direction
E
STREET_NAME
FRONTAGE
STREET_TYPE
RD
City
RIPON
Zip
95366
APN
26102004
CURRENT_STATUS
01
SITE_LOCATION
1022 E FRONTAGE RD
P_LOCATION
05
P_DISTRICT
005
QC Status
Approved
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SJGOV\sballwahn
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EHD - Public
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15 January 2001 <br /> AGE-NC Project No 98-0433 <br /> Page 4 of 5 <br /> ,y <br /> • Ground water at the site was encountered at approximately 18 50 to 22 20 feet bsg The <br /> prevailing ground water flow direction is generally toward the southwest with very low <br /> hydraulic gradients <br /> • The highest concentration of dissolved hydrocarbons quantified as TPH-g and TPH-d is in <br /> the area of monitoring well MW-1 located adjacent to the former UST area TPH-g and <br /> TPH-d concentrations in ground water decrease eastward in the area of well MW-7 and <br /> decrease south of the former USTs in the area of well MW-8 <br /> • The greatest concentration of benzene was detected in well MW-1 Benzene was also <br /> detected in MW-2 The benzene plume is fully defined by MW-4 to the north, MW-3 and <br /> MW-5 to the west, MW-8 to the south and MW-7 to the east <br /> • MTBE was detected in wells MW-1, MW-2, MW-3 and MW-4 at concentrations ranging as <br /> R high as 8,400µg11 The MTBE plume is generally defined by MW-8 to the south, MW-7 to <br /> the east, wells MW-3 and MW-5 to the west and to the north by well MW-4 (MTBE detected <br /> at 6 5 µg11) <br /> • D1PE and TBA were detected in well MW-8 at concentrations of 3 5 µgll and 11 ug/l, <br /> respectively = <br /> S.U. RECOMMENDATIONS <br /> Based on the results of this investigation AGE recommends the following <br /> • Quarterly monitoring at the site should continue to coincide with the monitoring performed <br /> at the Ripon Farm Service site The next monitoring event should be scheduled for January <br /> 2001 and should again include sampling of on-site domestic wells for analysis for <br /> constituents of concern <br /> • A work plan for installation of necessary wells to assess feasibility of various corrective <br /> action alternatives should be prepared The work plan should also detail procedures to assess <br /> the vertical limit of dissolved MTBE in the ground water At a minimum two soil borings <br />' should be advanced, with appropriate technology„to sample discrete ground water zones <br /> • A ,Corrective Action Plan (CAP) should be prepared upon completion of the feasibility <br /> testing and vertical assessment The CAP should include remediation feasibility studies (e g <br />' in-situ air sparging pilot test, soil vapor extraction soil excavation and bio-enhanced <br /> remediation or attenuation) to determine appropriate remedial options for the site The CAP <br />' should also include a well receptor survey to determine if local domestic water wells (beyond <br /> the domestic well that serves the Jimco site) may be at risk from the dissolved petroleum <br /> hydrocarbon plume at the site ` <br /> N <br /> Adiarreed(.eoEiivir1)IImcilial Inc <br /> 1 <br />
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