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ARCHIVED REPORTS XR0012562
EnvironmentalHealth
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2900 - Site Mitigation Program
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PR0536618
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ARCHIVED REPORTS XR0012562
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Entry Properties
Last modified
3/4/2019 10:37:51 AM
Creation date
3/4/2019 8:02:28 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0012562
RECORD_ID
PR0536618
PE
2960
FACILITY_ID
FA0021026
FACILITY_NAME
STOCKTON CHARTER WAY COMMON PLUME
STREET_NUMBER
440
Direction
W
STREET_NAME
CHARTER
STREET_TYPE
WAY
City
STOCKTON
Zip
95206
APN
16503003
CURRENT_STATUS
01
SITE_LOCATION
440 W CHARTER WAY
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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F <br /> w <br /> y <br /> 'i <br /> J U L 1 9 '"lt <br /> ENVIRONMENTAL HEALTH <br /> Mr. R.R.Zielinski PERMIT/2111010551 <br /> 02320 0 0475 Page 2 <br /> The water samples were analyzed using modifier! EPA methods 5030/8020/8015, which measure <br /> concentrations of total petroleum hydrocarbons-as-nasoline(rPH-G),and benzene,toluene,ethylbenzene <br /> and xylenes(BTEX). Copies of the laboratory analysis reports and chain-of-custody manifest are presented <br /> in Attachment C. <br /> GROUNDWATER ANALYYICAL RESULTS <br /> Concentrations of TPH-G in the groundwater samples ranged from 240 parts per billion(ppb)to 83,000 ppb; <br /> the range for the previous quarter was from 640 to 84,000 ppb. Two mr;Aoring wells recorded substantial <br /> changes in dissolved TPH-G concentrations, MW-4 decreased frcrn 84,U04 to 38,OQC"ppb and MW-5 <br /> Increased from 30,000 to 83,000 ppb TPH-G. The benzene concentrations ranged from 0.9 to 21,400 ppb. <br /> TPH-G and benzene concentrations in groundwater for February 8, 1991 are shown in Figures 2 and 3 <br /> (Attachment A). Table 2(Attachment B),presents results of the laboratory analyses for the last five sampling <br /> events. <br /> SOiL VAPOR EXTRACTION TEST <br /> BACKGROUND <br /> Analytical results of soil samples collected from 15 soil borings, and an angle boring, Installed during the <br /> course of the subsurface Investigation,were used to define the extent hydrocarbon Impacted soils beneath <br /> the Texaco service station site. Those soil samples were analyzed by a State-certifiad laboratory. Fifteen <br /> of the samples collected contalneJ detectable concentrations of TPH-G ranging from 2 to 2,500 parts per <br /> million (ppm);9 samples contain ld detectab:e concentrations of benzene ranging from 1 to 11 ppm. <br /> Based on the laboratory analyses of the soil samples, hydrocarbon-Impacted soil appears to be confined <br /> beneath the northeast corner of the site and has been defined in all directions except to the north, <br /> underneath Charter Way. Assuming that the Impacted soil does not extend further than 20 feet north of the <br /> site, (under Charter Way),the vo€vme of impacted soil is estimated to be approximately 3,000 cubic yards. <br /> The average concentration of petroleum hydrocarbons in the soil has been estimated io be between 500 <br /> and 1,000 parts per million(ppm)yielding a total weight of hydrocarbons between 4,300 and 8,700 pounds. <br /> Since Charter Way Is StatQ Route 4 and within the Cal Trans right cf way,further subsurface exploration Is <br /> not feasible because Cal Trans does not allow this type of encroachment. <br /> Soils encountered during drilling operations consisted predominately of clay to a depth of 30 to J5 feet <br /> below ground surface(BGS). The clay is underlain by water-bearing s€It and a fine micaceous sand. <br /> SOIL VAPOR EXTRACTION PILOT TEST METHOD <br /> A soil-venting pilot test was conducted on May 21, 1991. Permisslon was obtained from the San Joaquin <br /> County Air Pollution Control District prior to conducting the test. The test was conducted to determine the <br /> radius of Influence and the concentration of hydrocarbons in the soil vapor extracted from MW-1,MW-4 and <br /> MW-S. Vapors were drawn from each extraction well by a 1.5 horsepower regenerative blower. Flow rate <br /> during the test was monitored with a Kurz model 441 air velocity meter,and wau varied between 10 and 63 <br /> cubic feet per minute (cfm). Effluent air from the blower was discharged directly to the atmosphere and <br /> concentraticns were monitored during operation with a portable photo-Ionization detector(PID). A sample <br /> from extraction wells MW-5 and MW-4 was collected in Tedlar bags and shipped with a chain-of-custody <br /> manifest to GTEL for analysis according to EPA methods 5030/8015/8020 for BTEX,and TPH-G. No sample <br /> was collected from MWA because of the presence of separate-phase petroleum in the well. <br /> l'� GROUNIMIMt•:It <br /> TFumoi.ocy.isc. <br />
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