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SITE INFORMATION AND CORRESPONDENCE_2001-2005
Environmental Health - Public
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SITE INFORMATION AND CORRESPONDENCE_2001-2005
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Last modified
3/31/2020 2:57:43 PM
Creation date
3/31/2020 2:38:19 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
FileName_PostFix
2001-2005
RECORD_ID
PR0506203
PE
2960
FACILITY_ID
FA0007271
FACILITY_NAME
LINCOLN CNTR ENV REMEDIATION TRUST
STREET_NUMBER
0
STREET_NAME
PACIFIC
STREET_TYPE
AVE
City
STOCKTON
Zip
95207
CURRENT_STATUS
01
SITE_LOCATION
PACIFIC AVE
P_LOCATION
01
P_DISTRICT
002
QC Status
Approved
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Lincoln Center, Stockton • 0 w <br /> Revised Draft Feasibility Study - 2 - February 13, 2003 <br /> The soil RAO is to reduce the mass of Hazardous Substances in soil and soil vapor to <br /> concentrations that (1)would result in an indoor-air-inhalation risk of less than or equal <br /> to 10-5 excess lifetime cancer risk of a hypothetical worker and(2)result in a <br /> concentration of Hazardous Substances in groundwater at concentrations less than or <br /> equal to MCLS. <br /> Use of the hypothetical worker exposure scenario can only be used in conjunction with a <br /> selected remedy that includes institutional controls such as deed restrictions to assure no <br /> future residences, schools or hospitals are constructed on the site. We note that the"point of <br /> departure"in the NCP is an excess cancer risk level of 10-6. Use of the 10-5 excess cancer <br /> risk level must be justified. Lastly,under Board requirements, resulting concentrations in <br /> groundwater must be as low as technically and economically feasible. In no case, can <br /> resulting concentrations be greater than MCLS. The RAOs should be revised to incorporate <br /> these concepts. <br /> 3. Section 2.3.1 entitled"RAOs Based on Indoor-Air Inhalation" again improperly uses a <br /> worker based exposure scenario. The FS should include the details and assumptions used in <br /> the calculation of allowable air concentrations and the vapor-transport modeling. The <br /> sensitivity of the model to a reasonable range of values for each input parameter into the <br /> model should be presented and discussed. <br /> 4. Section 2.3.2 entitled"RAOs Based on Groundwater" indicates that analytical modeling was <br /> performed using EPA's Soil Screening Guidance. We do not currently accept the use of soil <br /> screening levels developed using that guidance. RAOs should be developed using site <br /> specific parameters, input into a vadose zone contaminant transport model such as VLEACH. <br /> RAOs should be based on leachate concentrations, as predicted by the model, without <br /> inclusion of dilution of leachate by the groundwater. <br /> 5. Section 2.4 entitled"Remedial Action Objectives for Groundwater" again improperly uses a <br /> worker based exposure scenario. Also,reference is made to MCLs as the RAO when, under <br /> Board requirements, resulting concentrations in groundwater must be as low as technically <br /> and economically feasible. Equations, assumptions, etc. used in the back-calculated health- <br /> based RAO should be provided. <br /> 6. On pages 103 and 109, under the paragraphs entitled"Reduction of Total Mass of Hazardous <br /> Substances",the document states that the RAO for vadose-zone soils is 150 ug/1 for PCE in <br /> soil gas. Please see our comments above regarding the development of an appropriate RAO <br /> for vadose-zone soils. <br /> 7. The"Recommended Remedial Plan"is described in Section 6 of the document. The <br /> recommended is Alternative 4 that involves the following activities: <br /> • vadose-zone source reduction through continued operation of the Soil Vapor extraction <br /> and treatment system, <br /> • continued operation of the groundwater extraction and treatment system, <br /> • A-zone groundwater source reduction, and <br />
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