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ARCHIVED REPORTS_XR0003259
Environmental Health - Public
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ARCHIVED REPORTS_XR0003259
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Last modified
2/11/2020 10:05:49 AM
Creation date
2/11/2020 8:44:46 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0003259
RECORD_ID
PR0545289
PE
3528
FACILITY_ID
FA0003828
FACILITY_NAME
VAN BUSKIRK GOLF COURSE
STREET_NUMBER
1740
STREET_NAME
HOUSTON
STREET_TYPE
AVE
City
STOCKTON
Zip
95206
APN
16307036
CURRENT_STATUS
02
SITE_LOCATION
1740 HOUSTON AVE
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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' 02 September 2003 <br /> AGE-NC Project No. 98-0468 <br /> ' Page 6 of 1 I <br /> MTBE was detected indiscrete groundwater samples collected from 55 feet bsg,approximately 100 <br /> ' feet down gradient from the former UST. The down-gradient lateral' .extent of petroleum <br /> hydrocarbons is limited by wells MW-7 and MW-8. <br /> ' During the last sampling event in April 2003, TPH-g was detected in ground water samples MW-6 <br /> and: MW-8 at concentrations of 290 µg/1 and 140 µgll, respectively. BTEX compounds.were not <br /> ' detected in any of the ground water samples.MTBE was detected in water-table-well samples MW-4 <br /> and MW-6 at concentrations 16 µg/1 and 120 µg/l, respectively. MTBE was also detected in deep- <br /> screened-well samples MW-9 and MW-10 concentrations of 80 ltg/l and 28 gg/l, respectively. <br /> ' Ground water data and analytical ground.water monitoring well data are included in Tables 3 and 4. <br /> 4.0. PROCEDURES <br /> On 17 July 2003, two soil boring (CPT1 and CPT2) were advanced on=site .(Figure 2). CPT <br /> ' technology was utilized at each boring location. Lithologic data was collected from the initial CPT <br /> boring and an immediately adjacent twin boring was then advanced to collect grab ground water <br /> • samples from selected depths. i <br /> ' 4.1. CPT LITHOLOGIC INVESTIGATION <br /> The CPT investigation utilized a 25-ton truck-mounted CPT drill rig equipped with 1.50-inch <br /> ' diameter hollow-stem rods. A hydraulic ram was utilized to advance a cone penetrometer tip <br /> attached to the hollow-stem rod assembly to total depth in each soil-boring. CPT1 was located at <br /> monitoring wells MW-4,MW-6 and soil boring SB8 and advanced to a depth of 125 feet bsg. CPT2 <br /> i ' was located north of monitoring well MW-10 and advanced to a depth of 105 feet bsg. <br /> At each boring location,the soil.parametersof cone penetrometer tip resistance, sleeve friction and <br /> pore water pressure were continuously measured as the cone penetrometer was advanced to.depth. <br /> Utilizing the soil parameters, the Hogentogler Co. computer program interpreted general lithology <br /> types based on the CPT Soil Behavior Classification System (Robertson, P.K., Campanella, R.G, <br /> ' Gillespie, D, and Greig, J., 1986).and displayed the interpreted lithologies on a continuous CPT <br /> boring log. The CPT interpretive logs are presented in Appendix B. <br /> ' Rinseate generated during drilling activities was containerized in properly labeled DOT-approved <br /> 55-gallon drums and'was stored on-site in an area lacking public access. The CPT soil borings were <br /> backfilled over their entire depth range with.a bentonite/Portland cement grout mix. <br /> ' Advanced GeoEnvironMental,Inc., <br />
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