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ARCHIVED REPORTS XR0000211
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1603
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3500 - Local Oversight Program
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PR0543430
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ARCHIVED REPORTS XR0000211
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Last modified
2/5/2019 11:25:37 AM
Creation date
2/5/2019 10:40:04 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0000211
RECORD_ID
PR0543430
PE
3528
FACILITY_ID
FA0009377
FACILITY_NAME
CAL TRANS MAINT SHOP 10
STREET_NUMBER
1603
Direction
S
STREET_NAME
B
STREET_TYPE
ST
City
STOCKTON
Zip
95206
APN
16918002
CURRENT_STATUS
02
SITE_LOCATION
1603 S B ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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SECTIONONIE Q®t®dooda <br /> 9.2 OBJECTIVES <br /> The primary objective of this risk analysis was to evaluate the potential impacts to groundwater and <br /> human health risks due to potential exposure to residual petroleum hydrocarbons which remain in the <br /> soil and groundwater The analysis was conducted in a "worst-case" manner to evaluate what the <br /> reasonable maximum exposure concentrations night be at a hypothetical well located 500 feet and <br /> 1,000 feet downgradient <br /> The results presented in this risk assessment specifically address potential health risks associated with <br /> ingestion of groundwater, mhalation of volatiles at the surface, dermal exposure to groundwater, and <br /> soul ingestion <br /> The purpose of this risk assessment and groundwater impact analysis was to assess current and <br /> potential future risk to human health and the groundwater The objective of the risk assessment <br /> and groundwater impact analysis was to provide an objective estimation of the potential current <br /> and future risk to human health and groundwater posed by the residual petroleum hydrocarbons in <br /> soil and groundwater If the risk levels are unacceptable, the risk assessment and groundwater <br /> impact analysis may be used for evaluating site-specific remedial action goals and making risk <br /> management decisions on acceptable levels of risk <br /> I <br /> Site-specific data were used whenever possible (Sections 3 and 4) This approach is consistent with <br /> the recently issued guidance by the U S Environmental Protection Agency (EPA) Risk Assessment <br /> Council stressing the use of site-specific data to evaluate potential health risks (EPA,1992a,b) <br /> Another objective was to follow the Risk Assessment Council's guidance for nsk characterization, <br /> limiting the discussion of information to risk assessment instead of including any risk management <br /> discussions, rdent4mg key uncertainties and their potential to under- or overestimate risk, and <br /> including information on a range of exposure W1uhe the reasonable maximum exposure (RME) is <br /> designed to be a measure of"high-end" exposure and is used by risk managers in makung remedial <br /> decisions(if any)to be protective to human health, the average or central tendency risks are necessary <br /> infonmatzon to make risk management decisions (EPA, 1992c) Conservative assumptions (i e, <br /> assumptions that generally overestimate risk)were used in tins assessment when site-specific data were <br /> lacking or incomplete <br /> 9.3 SCOPE <br /> The scope of this risk assessment is linuted to the evaluation of potential health risks and groundwater <br /> impacts associated with residual contarnuiants in soil and groundwater associated with the former <br /> gasoline tanks under existing conditions and projected future land use Future site development will <br /> T%1907W78008NAWOCKTOMREPORPSHOROVI D0C%&FEWM9730WNA%MA 14 <br />
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