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ARCHIVED REPORTS_XR0005453
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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N
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99 (STATE ROUTE 99)
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19256
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2900 - Site Mitigation Program
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PR0540323
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ARCHIVED REPORTS_XR0005453
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Entry Properties
Last modified
11/19/2024 1:50:27 PM
Creation date
4/8/2020 2:45:25 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0005453
RECORD_ID
PR0540323
PE
2950
FACILITY_ID
FA0023049
FACILITY_NAME
TELFER HIGHWAY TECHNOLOGIES
STREET_NUMBER
19256
Direction
N
STREET_NAME
STATE ROUTE 99
City
ACAMPO
Zip
95220
CURRENT_STATUS
01
SITE_LOCATION
19256 N HWY 99
QC Status
Approved
Scanner
SJGOV\sballwahn
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EHD - Public
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Mr Daniel K Barber, P E <br /> ' September 9, 2003 <br /> . Page G of 17 <br /> ■ Groundwater is or is not a known or potential drinking water source <br /> ' Land use is also taken into account The DLM and RBSLs are useful in that they reference <br /> hydrocarbons as both diesel (TPHd) and gasoline (TPHg) The subject site residual <br /> contamination is mainly in the form of TPHd, as shown in Table 1 <br /> ' Groundwater Contamination <br /> The RWQCB evaluates site contamination and its impacts on the environment on a case-by- <br /> case basis using various criteria, including existing land use designation, groundwater use, <br /> location of sensitive receptors, etc We understand that SJCEHD, as LOP to the RWQCB, <br /> generally follows RWQCB entena for assessing potential impacts to groundwater According <br /> to SJCEHD policy, groundwater is always considered potentially useable While the Region <br /> 5 RWQCB does not publish such guidance, it often screens sites for concentrations above 10 <br /> times the drinking water Maximum Contaminant Levels (MCLS) In the case of this site, the <br />' 10-times MCL screening for BTEX is not exceeded For the site contaminants of concern <br /> with published MCLS, only benzene and total xylenes have been detected (and only in "grab" <br /> groundwater samples collected from exploratory boreholes), they have never been detected in <br /> excess of their respective MCLs <br /> There are no drinking water MCLs for TPHg or TPHd When dealing with gasoline or diesel <br /> hydrocarbon contamination in groundwater, some RWQCBs will use RBSLs (or ESLs that <br /> are replacing them) to evaluate whether contamination warrants remediation and/or further <br />' investigation However, we understand from discussions with Mr Wong that the SJCEHD <br /> does not use nsk-based considerations as part of its closure criteria The primary criterion for <br /> selecting the appropriate groundwater RBSL is whether a current or potential drinking water <br />' source is threatened by the contamination While the State of California considers all <br /> groundwaters to be a potential drinking water source, as does SJCEHD, until a site-specific <br /> variance has been obtained, it is our understanding that groundwater is not used as drinking <br /> water in this area due to high total dissolved solids/turbidity associated with the upgradient <br /> ' Victor Sausage site (Gallardo & Associates, 1999) While we understand that the <br /> groundwater RBSLs are not considered by SJCEHD, it can be instructive to examine the <br /> RBSLs for site contaminants such as TPHd and TPHg that have no MCLs <br /> ' RBSLs/ESLs are not clean-up goals, which should be determined based on potential risks to <br /> groundwater and human and ecological receptors (commonly via a risk-based assessment <br /> ' model) Reducing residual contamination to levels at or below RBSLs also does not <br /> necessarily allow for regulatory closure, that determination being up to SJCEHD Some site <br /> Stellar Environmental Solutions <br /> yyROlEC15003 M1 SYopNlOp)J0.pAp-ba We cb.iadAepuud FyunWEPORT-Sapmbsr A3001 doc <br />
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