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2900 - Site Mitigation Program
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PR0508450
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
5/29/2019 11:58:23 AM
Creation date
5/29/2019 11:10:41 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0508450
PE
2960
FACILITY_ID
FA0008087
FACILITY_NAME
DDJC-TRACY
STREET_NUMBER
25700
STREET_NAME
CHRISMAN
STREET_TYPE
RD
City
TRACY
Zip
95376
APN
25207002
CURRENT_STATUS
01
SITE_LOCATION
25700 CHRISMAN RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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Peter MacNiohdl <br /> February 2,2009. <br /> DDJC Site <br /> Page 2 <br /> embodied in DTSC's recommendations, Therefore, the receptors should be identified as the <br /> adult and child residents and the industrial worker. <br /> 2. Section 5.1.4, Exposure Scenarios, page 5-3 <br /> The discussion in this section is 'incorrect.. Exposure scenarios are residential and industrial. <br /> The exposure assessment uses the chemical data to estimate the exposure point concentration <br /> for each receptor under an assumedexposurescenario. HERD recommends that either this <br /> section is deleted or accurately discussed under"Exposure Characterization." <br /> 3. Section 5.4.2, Risk and Hazard Index Estimates,page 5-5 <br /> Please revise the identified receptors in accordance with specific comment 91. <br /> 4. Section 5.4.4.1 and Table 5-4 <br /> The risk assessment shows that the exposure route that is driving the risk is dermal contact and <br /> yet, the risk-based concentrations are based solely on ingestion and excludes dermal contact <br /> for the residential scenario. This presents an underlying inconsistency in the development of <br /> risk-based concentrations. HERD's recommendation is to calculate the risk-based <br /> concentrations by applying exposure assumptions similar to what were applied in estimating the <br /> baseline risks. <br /> 5. Appendix C, Section 2, Problem Formulation,C-1 <br /> There seems to be some confusion between the elements of an ecological risk assessment and <br /> of a human health risk assessment. To illustrate, Problem Formulation is the first element in a <br /> quantitative or semi-quantitative ecological risk assessment. The elements of a human health <br /> risk assessment, on the other hand, are Identification of Chemicals of Potential Concern, <br /> Exposure Assessment, Toxicity Assessment, and Risk Characterization. Therefore, the <br /> discussion in Section 2 is incorrect and should be revised accordingly. <br /> 6. Appendix C, Section 2.1, Exposure Pathway Analysis, pages-3, C-2, 2 nd paragraph <br /> The term"chemical stressor" is used in ecological, not in human health, risk assessments. <br /> A source of chemical release is one of four factors that define a complete exposure pathway. <br /> This paragraph should be modified so that a complete exposure pathway is accurately <br /> discussed. <br /> 7. Appendix C,Section 2.4, page C-4 <br /> Please see specific comment 1 regarding the identified receptors and revise the 'text <br /> accordingly. <br /> 8. Appendix C,Table C-4 <br /> The parameters in this Table indicate that the adult:resident was the only receptor assumed to <br /> have dermal contact with groundwater. An age-adjusted ingestion factor was incorporated into <br />
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