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ARCHIVED REPORTS XR0000211
EnvironmentalHealth
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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
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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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SECTIONF®UR RKPosumAss®ssmeng <br /> Residential populations were evaluated along with occupational employees to be conservative in the <br /> risk estimates, although EPA guidance indicates that it is not necessary to assume that future <br /> hypothetical residential receptors are located on the site or in the vicinity (EPA, 1989b) Residential <br />' receptors were assumed to be located 500 feet and 1,000 feet downgradient of the site (both in the <br /> wind and groundwater flow direction) <br /> 4.2 CONCEPTUAL SITE MODEL <br /> A Conceptual Site Model (CSM) shows all potentially complete exposure pathways for a source <br /> (Figure 4-1) The CSM identifies potential chemical sources, release mechanisms, transport media, <br /> routes of cherrucal migration through the environment, exposure media, and potential receptors Those <br />' exposure pathways that are significant are indicated as being complete, incomplete indicates those <br /> pathways in which contaminant intakes are considered to be relatively insignificant in comparison to <br />' other exposure pathways EPA guidance defines an insignificant pathway as one that has an exposure <br /> estimated to be two or more orders of magnitude less than by other pathways (for the same receptor), <br /> a pathway is also considered insignificant if the risks are much less for that pathway, or if the likelihood <br /> of exposure by that pathway is very small(EPA 1989b) <br /> For the Shop 10 site, the complete exposure routes relative to soil are from the residual contaminants <br /> in the subsurface which may volatilize to the surface and pose an inhalation risk Soil ingestion and <br /> dermal exposure to surface soils were also included in the risk calculations even though the site is <br /> paved where COCs in sort are located (Table 3-1) Additionally, the soil concentrations are <br /> significantly lower than EPA Region ]Xs health based PRGs for industrial soil PRGs take into <br /> account soil ingestion, dermal exposure to soil, and inhalation of volatiles and particulates assuming <br /> that there is no paving at the site (Section 3 3) Storm water erosion, sediment transport, and fugitive <br /> dust pathways are not consider kccomplete exposure pathways due to the depth of contamination and <br /> the 6 to 8 inches of paving at the site <br /> The potentially complete exposure pathways relative to groundwater include groundwater ingestion <br /> and inhalation of volatiles from groundwater The residual soil contamination may continue to leach to <br /> the groundwater and posel a groundwater ingestion risk if the water was used for beneficial purposes <br /> we. <br /> The closest groundwatef is orated approximately 1,000 feet cross gradient of the site and is screened <br />' at 500 feet bgs (Section 2 2) The District Manager of the California Water Service Company, Eric <br /> Mar, indicated that he is not aware of any hydraulic communication between the shallow aquifer and <br /> the deeper aquifer m the area of Shop 10 (E Mar Personal Communication, 1219198) <br /> i <br /> Wbo4We T%1997W79009NAWOCKTOMREPORT%SNQREPOI Docw*- &991873009NALSNA 4-2 <br />
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