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2900 - Site Mitigation Program
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PR0508043
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
5/24/2021 7:04:54 PM
Creation date
5/24/2021 11:28:39 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
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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Soil and Groundwater Investigation Report <br /> Vernalis Pump Station August 2006 <br /> • Conducted a search of California Department of Water Resources (DWR) files to obtain <br /> information on water supply wells and prepared a summary table,which is provided in this <br /> report. <br /> • Advanced six soil borings from which soil and groundwater samples were collected and tested by <br /> Lancaster Laboratories in Lancaster,Pennsylvania for the constituents of concern: BTEX by EPA <br /> Method 826013; TPHg by EPA Method 8015 Modified; TPHd(carbon range CIO to C25)by EPA <br /> Method 8015 Modified with and without silica-gel cleanup; and PAHs by EPA Method 8270C <br /> SIM. <br /> • Installed three groundwater monitoring wells. <br /> • Evaluated project data to determine the extent of affected soil and groundwater. <br /> • Prepared this Soil and Groundwater Investigation Report,which describes the investigation <br /> results and makes recommendations for future investigation activities. <br /> The field investigation was implemented in accordance with the RWQCB-approved work plan, except for <br /> the following variations: <br /> • Because site access could not be obtained from the owner of the San Joaquin Valley Hay <br /> Grower's Association(SJVHGA)property,which is located east and down gradient of the Arcos <br /> property,proposed borings SB-26 through SB-29 were not advanced. <br /> • Because flowing sands encountered during drilling made it impossible to collect high-quality grab <br /> groundwater samples from the borehole and to install monitoring well MW-6 in the borehole, a <br /> groundwater sample was not collected from boring SB-24. Instead,monitoring well MW-6 was <br /> installed in boring SB-23. <br /> For more information regarding the field and sampling methods employed during the field investigation, <br /> refer to Appendix A. <br /> 4. FINDINGS <br /> 4.1 SUBSURFACE CONDITIONS <br /> Soils encountered during the investigation ranged from low-plasticity clays and silts,to clayey or silty <br /> sands,to poorly graded sands and gravels with fine-grained sediments. Soil boring logs and monitoring <br /> well construction data are provided in Appendix B. <br /> Based on the depths at which saturated soils were noted on boring logs and the depths at which static <br /> water levels were measured in each borehole,the top of the uppermost groundwater ranged from <br /> approximately 30 to 35 feet bgs. Additionally,the shallow groundwater is unconfined. Because the top- <br /> of-casing elevations of the newly installed monitoring wells were surveyed at a later date, coinciding with <br /> subsequent groundwater monitoring and sampling activities,the direction and gradient of groundwater <br /> movement were not determined during the field investigation. However,based on the depth-to-water <br /> measurements of multiple quarterly groundwater monitoring and sampling events completed since this <br /> field investigation, it has been concluded that the shallow groundwater beneath the site flows to the east at <br /> a gradient of 0.001 ft/ft. <br /> 4.2 DWR FILE REVIEW RESULTS <br /> SAIC conducted a search of DWR files to identify water supply wells within a '/z-mile radius of the site. <br /> The search covered portions of Township 3-South,Range 6-East, Sections 24 and 34. <br /> AMEN <br /> 4 From Science to Solutions- <br />
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