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ARCHIVED REPORTS_SOIL MANAGEMENT PLAN
EnvironmentalHealth
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2900 - Site Mitigation Program
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PR0515455
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ARCHIVED REPORTS_SOIL MANAGEMENT PLAN
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Last modified
4/7/2020 3:01:30 PM
Creation date
4/7/2020 2:58:29 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
SOIL MANAGEMENT PLAN
RECORD_ID
PR0515455
PE
2960
FACILITY_ID
FA0012158
FACILITY_NAME
RIDGEWAY PROPERTY
STREET_NUMBER
1881
STREET_NAME
RUSTAN
STREET_TYPE
RD
City
TRACY
Zip
95376
CURRENT_STATUS
02
SITE_LOCATION
1881 RUSTAN RD
P_LOCATION
03
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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S 5.0 HUMAN HEALTH SCREENING EVALUATION GEOMATFIIX <br /> A health risk screening evaluation was conducted to assess the potential human health risks <br /> associated with residual petroleum constituents detected in soil and groundwater. This evaluation <br /> was conducted based on the methodology presented in the Human Health Screening Evaluation <br /> section of the Preliminary Endangerment Assessment Guidance Manual(PEA; Cal-EPA, 1994). <br /> The PEA evaluation consists of a compilation of methods,models, and assumptions commonly used <br /> by California and United States Environmental Protection Agencies(Cal-EPA and U.S.EPA)to <br /> quantify human health risk and hazard at a site. The PEA evaluation is intended to provide <br /> conservative estimates of the theoretical lifetime excess cancer risk and noncancer hazard index <br /> based on reasonable maximum exposure in a residential setting. It should be noted,however,that the <br /> site is currently vacant and it is anticipated that the future use of the property will be commercial. <br /> Potential likely receptors at the site include future on-site commercial workers and construction <br /> workers. Nonetheless,to avoid restricting land use,the PEA methodology was used to evaluate a <br /> hypothetical future residential receptor as a conservative measure. Exposure pathways considered in <br /> this evaluation include inhalation of volatile organic chemicals from soil and household water; <br /> inhalation of airborne dust from soil;ingestion of soil, surface water,and groundwater; and dermal <br /> contact with soil, surface water,and groundwater. For purposes of this evaluation, all equations and <br /> default input assumptions provided in the PEA were used. <br /> As discussed in Section 4.0,TPHd,TPHc,TPHg, and some PAHs have been detected in soil at the <br /> site; two PAHs have been detected in shallow groundwater. For purposes of this evaluation,all <br /> detected constituents in soil and groundwater were quantitatively evaluated;the maximum detected <br /> concentration for each constituent was conservatively used as the representative concentration. It <br /> should be noted,however,that TPH measurements were not directly included in this evaluation, as <br /> prescribed in the PEA. The toxicity of these petroleum mixtures is best described by the aggregated <br /> toxicity of key individual constituents in the mixture,such as BTEX and PAHs(Cal-EPA, 1994). <br /> Appendix C presents the equations,models, and input parameters used to calculate the theoretical <br /> lifetime cancer risk and noncancer hazard index from exposure to petroleum constituents detected in <br /> soil and groundwater on this site; all input assumptions were based on conservative default <br /> parameters provided in the PEA. As shown in Appendix C,the theoretical lifetime cancer risk for an <br /> adult and child resident is 1x10;this value is at the lower end of the acceptable risk range of 1x10 <br /> to 1x10 used by Cal-EPA and U.S. EPA for sites where remediation is considered(CCR Division <br /> 4.5,Title 22 §67500.15 and U.S. EPA, 1990). The noncancer hazard index for an adult and child <br /> . resident is 0.65;this value is less than 1,indicating that the predicted exposure to petroleum <br /> \\SF3\DEPTDATA\DOC SAFE\5000S\5650\BURNS\BURNS SOILGW RPT.DOC 4 <br />
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