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SITE INFORMATION AND CORRESPONDENCE_FILE 1
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SITE INFORMATION AND CORRESPONDENCE_FILE 1
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Last modified
3/16/2020 11:36:44 PM
Creation date
3/16/2020 2:10:33 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
SITE INFORMATION AND CORRESPONDENCE
FileName_PostFix
FILE 1
RECORD_ID
PR0541875
PE
2960
FACILITY_ID
FA0024017
FACILITY_NAME
CHEVRON SITE 306415
STREET_NUMBER
437
Direction
E
STREET_NAME
MINER
STREET_TYPE
AVE
City
STOCKTON
Zip
95202
APN
1392417
CURRENT_STATUS
01
SITE_LOCATION
437 E MINER AVE
P_LOCATION
01
QC Status
Approved
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EHD - Public
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. From:staff To: Erin Garner • Date:119196 Time: 11:40:47 • Page 5 of 11 <br /> Subject: Supplemental Instructions to Slate Water Board December 2, 1995, <br /> Interim Guidance on Required Cleanup at Low Risk Fuel Sites <br /> January 5, 1996 / Page 2 <br /> LOW RICA SOILS CASE <br /> Deflnitlon. <br /> 1) The leak has been stopped and ongoing sources, including free product, removed or remediated. <br /> The tank or appurtenant structure that leaked must be repaired or permanently closed per Chapter 7, <br /> Section 2672 of the UST regulations. Free product shall be removed to the extent practicable per <br /> Chapter 5, Section 2655 of the UST regulations. <br /> Free product or soil which contains sufficient mobile constituents (leachate, vapors, or gravity flow) to <br /> degrade groundwater quality above water quality objectives or result in a significant threat to human <br /> health or the environment should be considered a source. <br /> For old releases, the absence of current groundwater impact is often a good indication that residual <br /> concentrations present in the soil are not a source of pollution. In general, it impacted soil is not in <br /> contact, or expected to come in contact, with or very close to the groundwater, it is unlikely that a is a <br /> significant source of pollution. <br /> 2) The site has been adequately characterized. <br /> The extent of the subsurface impact should be defined to the degree that is necessary to determine if the <br /> site poses a threat to human health, the environment, or other sensitive nearby receptors. The level of <br /> detail required at a given site will depend upon the presence or absence of potential receptors and <br /> exposure pathways. Delineating plumes to non-detect levels is not required at all sites. <br /> It is assumed that subsurface conditions are highly variable and that there is always some uncertainty <br /> associated with evaluating data at a site. However, the cost of obtaining additional data must be <br /> weighed against the benefit of obtaining that data and the effect the data may have on the certainty of <br /> decisions to be made at the site. <br /> 3) Little or no groundwater impact currently exists and no contaminants are found at levels above <br /> established MCLS or other applicable water quality objectives. <br /> By definition, soils only cases do not have significant groundwater impacts. <br /> 4) No water wells, deeper drinking water aquifers, surface water, or other sensitive receptors are likely <br /> to be impacted. <br /> 5) The site presents no significant risk to human health. <br /> The American Society of Testing and Materials' (ASTM) standard for Risked Based Corrective Action <br /> (RBCA), ASTM E-1739-95, details a framework and provides a methodology to perform a tiered risk <br /> analysis at petroleum release sites. This methodology incorporates EPA risk assessment practices to <br /> determine non-site specific (tier 1 look up table which provides generic risk based screening levels) and <br /> site specific (tier 2 and tier 3) clean up levels that are protective of public health and environmental <br /> resources. <br />
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