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4800 – General/Other Program
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PR0508043
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Last modified
5/24/2021 11:19:37 AM
Creation date
5/24/2021 10:29:31 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4800 – General/Other Program
File Section
FIELD DOCUMENTS
RECORD_ID
PR0508043
PE
2960
FACILITY_ID
FA0007905
FACILITY_NAME
CHEVRON PIPELINES
STREET_NUMBER
35500
STREET_NAME
WELTY
STREET_TYPE
RD
City
VERNALIS
Zip
95385
APN
25526003
CURRENT_STATUS
01
SITE_LOCATION
35500 WELTY RD
P_LOCATION
99
QC Status
Approved
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SJGOV\dsedra
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EHD - Public
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No Further Action Required Request Report <br /> US Can—Welty Road September 24,2013 <br /> and vertical extent of dissolved hydrocarbons in groundwater as effectively as any active <br /> remediation technology. Natural attenuation is a viable technology for weathered heavy-crude <br /> oil with low concentrations of BTEX, and where the extents of BTEX and associated TPH <br /> plumes in groundwater are generally limited to the area of SPO,as is typically the case at former <br /> OVP and TAOC sites. For most of the other technologies evaluated, "the costs to implement the <br /> technologies may exceed the value of the land and any improvements." Natural attenuation is <br /> generally cost free. <br /> The time required for natural attenuation to reduce TPH concentrations below WQOs, and then <br /> below background levels, could be lengthy and cannot be reliably estimated. An extended period <br /> of time does not pose a concern, as use of the shallow groundwater is unlikely given its likely <br /> low yield and poor quality. <br /> 15. Provide a discussion (and estimate) of contaminant mass remaining in soil and <br /> groundwater versus contaminant mass removed or destroyed by soil excavation or <br /> remedial actions. <br /> This item is not applicable because active site remediation has not been implemented or <br /> recommended. Natural attenuation will continue to reduce the COPC concentrations in soil and <br /> groundwater over time, as discussed in item 14. <br /> 16. Provide assumptions,parameters, calculations, and the model used in any risk <br /> assessments. <br /> SAIC calculated an estimated risk and hazard for the HHSE using the equations and assumptions <br /> outlined in the PEA Guidance Manual under the residential exposure scenario (the most <br /> conservative exposure scenario). The calculated exposure point concentrations for the COPCs <br /> are considered protective of a potential resident. See the summary of the HHSE in section 2.1 of <br /> this report for details regarding the assumptions,parameters, calculations, and model used in the <br /> HHSE(provided as Appendix B.24). <br /> 17. Provide assumptions,parameters, calculation, and the model used in fate and transport <br /> modeling. <br /> Fate and transport modeling has not been performed. <br /> 18. Provide a rationale why the conditions remaining at the site will not adversely impact <br /> water quality, human health and safety, or other beneficial uses The rationale for NFAR <br /> must include a finding about present and future water use, and risks the site may still <br /> represent to human health and safety, and water quality. <br /> Please see Section 4—Conclusions and Recommendations. <br /> 19. Provide a list of technical reports submitted for site assessment, corrective action, <br /> confirmation sampling,and closure. <br /> A list of references is provided in Section 5. <br /> 20.Provide any additional comments supporting site NFAR. <br /> See Section 4—Conclusions and Recommendations. <br /> 10 SAIE <br />
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