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2900 - Site Mitigation Program
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PR0543467
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Last modified
5/4/2020 4:18:47 PM
Creation date
5/20/2019 9:20:43 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0543467
PE
2960
FACILITY_ID
FA0024672
FACILITY_NAME
FORMER ATLANTIC RICHFIELD CO (ARCO) NO 6100
STREET_NUMBER
25775
Direction
S
STREET_NAME
PATTERSON PASS
City
TRACY
Zip
95377
CURRENT_STATUS
01
SITE_LOCATION
25775 S PATTERSON PASS
P_LOCATION
03
QC Status
Approved
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EHD - Public
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Mr.Nuel Henderson,P.G., SJCEHD September 21,2005 <br /> ARCO Station 6100,Tracy,California Project No.U6100-15-1 <br /> Additional Site Assessment Work Plan <br /> Page 5 <br /> Site Hydrogeology <br /> Based on information collected during the drilling of boring B-32, the regional water <br /> table appears to be deeper than approximately 202 feet bgs at the site. The on-site water <br /> supply well is screened between approximately 396 and 416 feet bgs and 496 to 536 feet <br /> bgs, with a gravel pack installed from approximately 35 to 540 feet bgs. The static water <br /> level in the water supply well has been measured at approximately 45 feet bgs. Based on <br /> this information, the water supply well appears to be screened within a confined regional <br /> water supply aquifer. <br /> Historical depth to groundwater measurements and groundwater elevations are presented <br /> in Table 3. The source of the groundwater observed in the monitoring and vapor <br /> extraction wells beneath the site cannot be positively determined at this time. In the site <br /> conceptual model (SCM), Stratus identified percolation of meteoric water into the <br /> subsurface, leakage from on-site water pipes, and recharge from the on-site water supply <br /> well as possible sources of the encountered groundwater. <br /> Stratus has previously reported that the water encountered in the shallow-screened wells <br /> was likely meteoric water. The basis of this interpretation was a general increase in water <br /> levels in the shallow screened wells during the winter and spring months, and decrease in <br /> water levels during the summer and autumn months. Groundwater elevations in the <br /> shallow screened wells were measured between approximately 223 and 258 feet msl at the <br /> time of the second quarter 2005 monitoring event. This significant variation in the water <br /> level measurements suggests that groundwater in the shallow screened wells is perched and <br /> localized. <br /> Depth to groundwater was measured between approximately 181 and 185 feet msl in the <br /> deeper screened monitoring wells located south of Patterson Pass Road. A review of <br /> Figure 6 shows approximately evenly spaced potentiometric surface lines, with a <br /> groundwater surface sloping towards the east-southeast at an average gradient of 0.031 ft/ft. <br /> Based on this observation, an upgradient source of groundwater recharge, providing <br /> relatively constant head pressure, appears to be supplying groundwater to sand zone 2. <br /> Given the groundwater elevations observed in wells MW-1, MW-12, MW-13, and MW-15, <br /> and the close, upgradient position of the on-site water supply well relative to these wells, it <br /> appears likely that groundwater recharge into sand zone 2 has occurred from the on-site <br /> water supply well. Since the well is gravel packed up to 35 feet bgs, and has a static water <br /> level of approximately 45 feet bgs, static water from the water supply well should come <br /> into contact with sand zone 2. However, the consistent absence of groundwater in deeply <br /> screened wells MW-3 and MW-7, which are situated between the on-site water supply well <br /> and off-site wells MW-1, MW-12,MW-13, and MW-15, is problematic to this explanation. <br /> K:\Bp-Arco for URS\6100\Work P1ans\wco6I00-workplan 09-2005.doc <br />
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