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2900 - Site Mitigation Program
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PR0542109
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Last modified
7/23/2026 1:33:33 PM
Creation date
3/11/2026 11:28:55 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0542109
PE
2960 - RWQCB LEAD AGENCY CLEAN UP SITE
FACILITY_ID
FA0024185
FACILITY_NAME
FORMER THRIFTY OIL CO STATION NO 172
STREET_NUMBER
7647
STREET_NAME
PACIFIC
STREET_TYPE
AVE
City
STOCKTON
Zip
95207
APN
07748014
CURRENT_STATUS
Active, billable
QC Status
Approved
Scanner
SJGOV\gmartinez
Supplemental fields
Site Address
7647 PACIFIC AVE STOCKTON 95207
Tags
EHD - Public
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Former Thrifty Co.Station No.172 <br /> Workplan for Additional Soil and Groundwater Assessment <br /> May 8,2017 <br /> be dependent on lithology observed during the drilling activities. Once the appropriate <br /> length of casing and well screen are installed, a filter pack consisting of #3 sand or <br /> equivalent will be emplaced in the annular space surrounding the well casing, <br /> extending approximately two feet above the top of the well screen, over which, a 3-foot <br /> thick layer of hydrated bentonite chips will be placed. The remainder of the annular <br /> space will be backfilled with cement grout to a depth of approximately one foot bgs. <br /> The well casing will be set within flush-mounted traffic-rated well vault. General field <br /> procedures are included in Appendix B. <br /> One monitoring well proposed to be screened in the shallow zone will be installed at <br /> the location shown on Figure 3. The borehole will be advanced using 8-inch diameter <br /> hollow stem auger drilling equipment and completed with 2-inch diameter schedule 40 <br /> PVC casing, with a well screen consisting of 0.010-inch slot screen. Based on <br /> previous site assessment activities, ATC's recommended monitoring well construction <br /> details are presented in Table 1; however, the precise depth and screened interval of <br /> the monitoring well will be dependent on lithology observed during the drilling activities. <br /> Once the appropriate length of casing and well screen are installed, a filter pack <br /> consisting of#3 sand or equivalent will be emplaced in the annular space surrounding <br /> the well casing, extending approximately two feet above the top of the well screen, <br /> over which, a 3-foot thick layer of hydrated bentonite chips will be placed. The <br /> remainder of the annular space will be backfilled with cement grout to a depth of <br /> approximately one foot bgs. The well casing will be set within a flush-mounted traffic- <br /> rated well vault. General field procedures are included in Appendix B. <br /> • Sample Selection and Analysis. Soil samples will be collected at 5-foot intervals, <br /> from the borings for logging purposes and samples will be sent under chain-of-custody <br /> procedures to a California State-certified laboratory. At least two samples from each <br /> boring will be analyzed for TPPH (a.k.a. TPHg), BTEX, MTBE, ETBE, TBA, TAME, <br /> DIPE, EDB, 1,2-DCA and ethanol by EPA Method 8260. At least one soil sample will <br /> be analyzed for Title 22 Metals to establish background metals concentrations. A <br /> composite soil sample will also be collected and analyzed for soil profiling and disposal <br /> purposes. <br /> • Well Development and Surveying. The monitoring well will be developed by <br /> rigorously surging the well over the length of the screen interval and by purging until <br /> the extracted groundwater is deemed clear (up to a maximum of 10 casing volumes of <br /> water from the well). Following installation activities, the newly installed monitoring <br /> well will be surveyed by a licensed surveyor to a local benchmark relative to mean sea <br /> level. Survey data including elevation, longitude, and latitude will be uploaded to the <br /> state GeoTracker database. <br /> • Soil Boring Advancement. ATC will contract with a C-57 licensed drilling company to <br /> advance one exploratory soil boring in the immediate vicinity of the former waste oil <br /> tank using direct push technology (Figure 2). Soil will be collected from the boring for <br /> lithologic logging and field screening using a 4-foot by 1.5-inch outside diameter core <br /> sampler equipped with an acetate liner. Soil samples will be screened using a photo- <br /> ionization detector (PID) and any noticeable staining will be noted. Soil samples for <br /> Iithological description will be collected at 4-foot intervals to the total depth explored, <br /> approximately 20 feet bgs. The soil boring will then be grouted to the surface by <br /> 8 <br />
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