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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
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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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ChevronTexaco—Vernalis Pump Station,Vernalis,CA. Project No. 06-6102-00-6369-201 <br /> June 29,2004 Page 5 of 7 <br /> according to SJCPHS/SCDER requirements and advance contingency borings at the locations shown on <br /> Figure 2. Based on the analytical results from the Geomatrix Report of Soil and Groundwater <br /> Investigation, dated January 5,2004, SAIC is planning five contingency borings to define the lateral <br /> extent of affected soil and groundwater. Following completion of the soil borings,the open boreholes <br /> will be destroyed according to SJCPHS/SCDER requirements. <br /> Soil samples will be submitted to a California State-certified laboratory,Lancaster Laboratories <br /> (Lancaster)in Lancaster, Pennsylvania(ELAP#2501),under proper chain-of-custody protocol. Selected <br /> soil samples will be analyzed for BTEX by U.S. Environmental Protection Agency(EPA)Method 8021B, <br /> TPHc by EPA Method 8015 modified, and PAHs by EPA Method 8270C Select Ion Monitoring(SIM). <br /> SAIC will also obtain grab groundwater samples from select soil borings and submit them to Lancaster <br /> under proper chain-of-custody protocol for the following chemical analyses: BTEX by EPA Method <br /> 826013; TPHg and TPHd by EPA Method 8015 modified; TPHd by EPA Method 8015 modified with <br /> silica-gel cleanup; and PAHs by EPA Method 8270C SIM. <br /> TASK 4—WELL INSTALLATION,QUARTERLY GROUNDWATER MONITORING AND <br /> SAMPLING <br /> SAIC is recommending the installation of five groundwater monitoring wells(MW-5 through MW-9)to <br /> be incorporated into a quarterly monitoring and sampling program with the four existing groundwater <br /> monitoring wells (MW-1 through MW-4)located northwest of the former pump house. SAIC is <br /> proposing additional wells and initiating a monitoring and sampling program of 4 quarters to establish a <br /> chemical data base to verify that residual contamination beneath the site is stable and confined to the <br /> proposed investigation limits to be determined. In addition,the installation and sampling of groundwater <br /> monitoring wells will provide a higher quality groundwater sample that will enable the analytical <br /> laboratory to achieve the needed detection limit required by the Department of Toxic Substances(DTSC) <br /> for use in a Human Health Screening Evaluation(HHSE). If groundwater sampling results are consistent <br /> and the residual petroleum beneath the site is stable and confined throughout one hydrological cycle, <br /> SAIC will recommend additional sampling is not warranted and request the site be considered for"No <br /> Further Action"(NFA). It is understood that a NFA status will only be granted by the RWQCB following <br /> an evaluation of the HHSE by DTSC. <br /> Task 4.2—Installation of Groundwater Monitoring Wells <br /> Four groundwater monitoring wells are being proposed northeast of previous borings SB-19 and SB-20, <br /> and northeast of proposed borings SB-27 and SB-28. An additional well is proposed west(up gradient) <br /> of the former western Aboveground Storage Tank(AST)to be an up-gradient measuring point for depth <br /> to groundwater and to define up-gradient chemical concentrations. During advancement of soil borings <br /> east-northeast(down gradient)of the former pump station, SAIC will evaluate each borehole as described <br /> in Task 3. If a significant interval of affected soil is observed in the primary borings, SAIC will drill a <br /> contingency boring further down gradient. SAIC intends to construct monitoring wells in areas where <br /> affected soil is not observed. Monitoring well locations are shown on Figure 2. <br /> The proposed groundwater monitoring wells will be constructed of 2-inch diameter, flush-threaded, <br /> Schedule 40 polyvinyl chloride (PVC)well casing with 20 feet of 0.010-inch machine slotted well screen <br /> backfilled with Monterey 2/12 sand. The well seal will be constructed with a bentonite transition seal and <br /> neat cement containing approximately 5 percent bentonite to surface grade. The well head will be <br /> completed above ground and protected with steel bollards. Well construction details are presented on <br /> Figure 3. After installation,the new monitoring well locations will be surveyed by a licensed surveyor <br /> for horizontal locations and top of casing vertical elevations. The survey of the newly installed wells will <br /> incorporate existing site wells. Following well construction, SAIC will develop and sample the wells in <br />
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