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12 (STATE ROUTE 12)
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13889
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3500 - Local Oversight Program
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PR0545719
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SITE HISTORY
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Last modified
11/19/2024 3:47:36 PM
Creation date
6/3/2020 11:22:17 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
SITE HISTORY
RECORD_ID
PR0545719
PE
3528
FACILITY_ID
FA0005335
FACILITY_NAME
CHARLES JACOBS
STREET_NUMBER
13889
Direction
W
STREET_NAME
STATE ROUTE 12
City
LODI
Zip
95240
CURRENT_STATUS
02
SITE_LOCATION
13889 W HWY 12
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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EHD - Public
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22 October 2009 <br /> AGE-NC Project No. 00-0697 <br /> Page 5 of 10 <br /> 2.4. GROUND WATER MONITORING:EVENTS <br /> Between November 2004 and October 2008,seventeen(17)ground water monitoring events were <br /> performed at the site to monitor dissolved petroleum hydrocarbon concentrations in ground water <br /> and to characterize ground water flow direction and gradient.on the site. Since initiation of the <br /> ground water monitoring program,ground water elevations ranged between 16.58 feet to 21.03 feet <br /> below the North American Vertical Datum(NAVD);depths to ground water ranged between 2.56 <br /> to 6.82 feet below the tops of the well casings(btoc)..From November 2004 to August 2005, and <br /> from August 2007 to October 2008, ground water flow direction at the site was inferred to be <br /> generally towards the north,at hydraulic gradients ranging between 0.007 fr/ft and 0.4 ft/ft.Between, <br /> November 2005 and May 2007 ground water flow direction at the site was inferred to range between <br /> the west and south at hydraulic gradients between 0.007 ftJft and 0.01 ft/ft.Ground water elevation <br /> data is summarized in Table 4. Ground water elevation figures depicting ground water flow <br /> directions and gradients from November 2004 to October.2008 are presented in Appendix D. <br /> Based on quarterly ground water monitoring results between November 2004 and October 2008, <br /> TPH-g and benzene were established as the contaminants of concern at the site(Table 5). Between <br /> February 2005 and February 2008, TPH-g and benzene concentrations were detected from well <br /> MW-3 at concentrations as high as 3,300 pg/I and 490 µg/l, respectively. However, TPH-g and <br /> benzene have not been detected from well MW-3 since May 2008 and February 2008,respectively. <br /> Laboratory analysis of ground water samples only detected TPH-g and benzene on one occasion from <br /> wells MW-1, MW-2, and MW-5; TPH-g and benzene have never,been detected above laboratory <br /> reporting limits from wells MW-4 and MW-6. Ground water monitoring well analytical data is <br /> summarized in Table 5. <br /> Based on a plot of TPH=g and benzene versus time(Appendix E),a definitive trend of decreasing <br /> dissolved concentrations is evident at the site from monitoring well MW-3. <br /> 2.5. STRATIGRAPHY <br /> In general,moist,black peat and silty peat were encountered from surface grade to 5 feet bsg across <br /> most of the site. However,peat and silty peat were encountered from surface grade to 9.5 feet bsg <br /> in the area of well MW-2.Additionally,fill dirt was encountered in boring MW-3 from surface grade <br /> to approximately 5 feet bsg. Silty clay, sandy clay, and clayey silt were generally encountered in <br /> borings MW-1,MW-3 and MW4 from 5 feet bsg to approximately 15 feet bsg,in boring MW-2 <br /> from 9.5 feet bsg to approximately 15 feet bsg, and in boring MW-6 from 5 feet bsg to <br /> approximately 20 feet bsg. Silty fine sand was encountered.froml 5 feet bsg to the;total depths of <br /> borings MW-1 through MW-4 and from 20 feet bsg to approximately 29 bsg in boring MW-6. A <br /> layer of moist clay was identified between 29 feet and 31 feet bsg..From 31 feet bsg to the total depth <br /> Advanced G mEavironmental,Inc. <br />
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