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SITE INFORMATION AND CORRESPONDENCE 1995-2004
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PR0524492
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SITE INFORMATION AND CORRESPONDENCE 1995-2004
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Last modified
2/25/2019 6:15:28 PM
Creation date
2/25/2019 2:39:14 PM
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
FileName_PostFix
1995-2004
RECORD_ID
PR0524492
PE
2959
FACILITY_ID
FA0016428
FACILITY_NAME
PACIFIC GAS & ELECTRIC
STREET_NUMBER
535
Direction
S
STREET_NAME
CENTER
STREET_TYPE
ST
City
STOCKTON
Zip
95203
APN
13732002
CURRENT_STATUS
01
SITE_LOCATION
535 S CENTER ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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0- <br /> James L. Tjosvold, P.E. <br /> August 19, 1996 <br /> Page 2 <br /> the combined soil and groundwater FS will include the information discussed <br /> below. The agency comments are italicized and presented before each response. <br /> Responses to DTSC comments (dated December 26,1995): <br /> Comment: <br /> 1. The FS Workplan has failed to define a criteria to establish soil cleanup levels that would <br /> be protective of groundwater. In order to safeguard water quality, a site-specific and resource <br /> protective criteria must form the basis for soil cleanup. The criteria then must be applied for <br /> all soil analytical data to determine the degree to which the site should be cleaned or remedial <br /> action is necessary. The RWQCB "Designated Level Methodology"for cleanup level <br /> determination, or its equivalent, must be used to support this criteria for establishing <br /> remedial action goals far soil. Based on application of the cleanup criteria, supported by a <br /> qualitative site analysis, contaminant source areas can be appropriately characterized and <br /> defined for the proposed remedial actions to be applied and remedial action goals to be <br /> satisfied. As a result of applying the above criteria, estimated volumes of contaminated soil <br /> requiring remediation may change, resulting in the need for re-evaluation of alternatives and <br /> thus requiring a major modification to the FS. <br /> Response: <br /> 1. The draft Soil OUFS report (not FS workplan) did not identify specific cleanup <br /> levels because of the nature and distribution of the COPC in the soil at the site. The <br /> COPC are immobile and distributed in random pockets throughout the site. The <br /> health and environmental risk assessment did not identify any significant(greater <br /> than 10-5 cancer risk or hazard index greater than one) human health risks at the site. <br /> Therefore, developing a site-specific criterion to be uniformly applied at the site <br /> most likely would result in massive treatment or excavation of the site with little or <br /> no overall risk reduction. For example, because small isolated concentrations can <br /> not be easily identified and treated, applying the beneficial use criteria for water <br /> provided by the RWQCB and back calculating soil cleanup criteria from those levels <br /> would result in a great amount of clean soil being treated to ensure that any isolated <br /> small pockets of contaminants are treated. It should be noted that many of the soil <br /> borings are located within ten feet of the next closest boring, thereby providing very <br /> detailed analytical coverage of the site. <br /> For these reasons, four qualitative criteria were applied to help identify areas <br /> requiring treatment. The overall goal was to treat the areas that have the greatest <br /> impact on groundwater quality. The qualitative criteria for defining soil source <br /> areas for treatment were presented in Section 5.2.2.2 of the draft OUFS as follows: <br />
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