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ARCHIVED REPORTS_XR0007203
EnvironmentalHealth
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3500 - Local Oversight Program
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PR0540315
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ARCHIVED REPORTS_XR0007203
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Last modified
7/7/2020 3:06:37 PM
Creation date
7/7/2020 2:31:11 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0007203
RECORD_ID
PR0540315
PE
3526
FACILITY_ID
FA0023046
FACILITY_NAME
U-HAUL FACILITY NO 710050
STREET_NUMBER
2701
Direction
N
STREET_NAME
WILSON
STREET_TYPE
WAY
City
STOCKTON
Zip
95215
APN
11708014
CURRENT_STATUS
01
SITE_LOCATION
2701 N WILSON WAY
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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Environmental Technology Inc .,_. <br /> Their report states that the soil sample "appears to contain a mineral spirit, <br /> Stoddard solvent, paint thinner, or an er li t dr based solvent. Me- <br /> -QW <br /> further states that the release occurred between four and twe ve years <br />' ago (i e.. 1984 to 1992) (Friedman & Bruya, 1995) Friedman & Bruya utilized <br /> capillary gas chromatography using a flame ionization detector (FID) to analyze <br /> the sample Using the FID, to analyze the soil sample, 10 ppm of TPH-d (EPA <br />' 8015M) was found in the sample. Their report notes that the material present <br /> is lighter than diesel #2 TPH-g and BTEX are also present in the soil sample <br /> (Table 2). A copy of the laboratory report is presented in Appendix C. <br /> 5.0 QUARTERLY M0MTORING <br />' As a part of on-going quarterly monitoring plan. SOTA s engineer measured the <br /> depth to groundwater at all eight monitoring wells (MW-1 through MW-8) on <br /> February 8, 1996 The depth to the water level and the corresponding surface <br /> elevations, with respect to mean sea level, are presented in Table 3 SOTA's <br /> engineer informed San Joaquin County Environmental Health Division of the <br /> proposed sampling event, in advance, on January 31, 1996 <br /> The sampling program was conducted as described below A minimum of 4 well <br /> casing volumes, which was calculated to be approximately 16 gallons, was <br /> purged from each of the eight wells During purging operations the <br /> temperature, pH, and conductivity were measured with the water flowing <br /> through a continuous flow chamber. The pumping was carried on until the <br /> temperature, pH, and conductivity values stabilized within at least 5% of <br /> previous readings Monitoring wells MW-1 through MW-8 were purged of <br />' approximately 25-gallons of water per well using a 2-inch submersible pump <br /> Copies of the field observation which includes temperature, pH, and <br /> conductivity values are enclosed in Appendix F Proper decontamination <br /> procedures which included flushing the pump and hose with a solution of <br /> detergent and water, followed by clean tap water, with a final rinse using <br /> deionized water were employed. The purged water is stored in 55-gallon DOT <br /> approved drums which have been labeled and stored on-site for subsequent <br /> treatment/disposal. Adequate time was allowed for recovery after purging All <br /> monitoring wells were allowed to recover to 95 percent or more of their static <br /> water level condition. At the time of groundwater sampling, neither free <br />' product nor sheen was noticed in any of the monitoring wells Dedicated <br /> bailers were used for sampling activities at each of the wells, in order to prevent <br /> possible cross contamination. <br /> The eight water samples were collected and stored in an ice chest maintained at <br /> 4° C. Appropriate chain of custody was prepared prior to transporting to a <br /> State certified laboratory. Del Mar Analytical, Irvine, CA performed the <br /> 1 laboratory analyses All the water samples were analyzed for Total Petroleum <br /> Hydrocarbons (TPH) as gasoline (Volatile Fuel Hydrocarbons) and Benzene, <br /> Toluene, Ethylbenzene, and Total Xylenes (BTEX) following EPA Methods <br /> 8015M/8020. The analytical results are presented in Table 4 <br /> 7 <br />
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