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2900 - Site Mitigation Program
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PR0536222
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Entry Properties
Last modified
9/5/2019 9:01:26 AM
Creation date
9/5/2019 8:44:29 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0536222
PE
2953
FACILITY_ID
FA0020812
FACILITY_NAME
RESIDENCE
STREET_NUMBER
1336
STREET_NAME
ESCALON
STREET_TYPE
AVE
City
ESCALON
Zip
95320
APN
22706109
CURRENT_STATUS
01
SITE_LOCATION
1336 ESCALON AVE
P_LOCATION
06
P_DISTRICT
004
QC Status
Approved
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EHD - Public
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• Mr.Harlin Knoll <br /> Page 2 of 4 <br /> Previous Soil Investigation <br /> Ms. Langum collected two soil samples at a depth of 6-inches below grade surface (bgs) and <br /> submitted the samples to CLS Laboratory located at 3249 Fitzgerald Rd, Rancho Cordova, CA <br /> 95742 (ELAP #1233) for analysis. The samples were analyzed for total petroleum hydrocarbons <br /> as diesel and as motor oil (TPHd and TPHmo, respectively). TPHmo was detected at <br /> concentrations of 110 and 210 milligrams per kilogram (mg/Kg) near the gas meter as shown in <br /> Figure 2. <br /> Soil Boring and Sample Collection <br /> On December 13, 2010, a Ground Zero technician measured and staked five sample points at <br /> approximately eight-foot intervals. At each sample point, the technician scraped away the 2- to <br /> 3-inches of the coarse sand cover to expose native soil and then using a hand auger advanced 6- <br /> inches. The technician then collected a 6-inch soil sample using a slide hammer sampling tool. <br /> This procedure was repeated at 12-inch intervals to a total depth of 3 feet bgs at each sample <br /> point. Soil samples were submitted to subjective analysis for contamination using a photo- <br /> ionization detector (PID) and the results are shown on Figure 2. Based on the results of the PID <br /> readings five soil samples were selected to be sent to a certified state laboratory for analysis. <br /> The samples were collected in brass tubes, sealed with Teflon tape, capped, uniquely identified, <br /> stored in an ice chest refrigerated to a temperature of approximately 4°C, and delivered under <br /> chain of custody protocol to Argon Laboratories (ELAP #2359) of Ceres, California (Argon) for <br /> analysis. <br /> RESULTS OF INVESTIGATION <br /> Subsurface Lithology <br /> The upper 3 feet of soil is predominately a fine grain sandy-silt overlain with 2- to 3-inches of <br /> coarse grain sand. There were no signs of soil staining visible to the sampling technician. There <br /> were no notable odors at any sampling point or sampling depth. <br /> Soil Analytical Results <br /> Five soil samples were selected and were submitted to Argon for analysis. The samples from the <br /> upper two feet were analyzed for TPHmo using EPA method 8015M. The remaining soil samples <br /> were analyzed for total petroleum hydrocarbons as gasoline(TPHg),TPHd, and TPHmo using EPA <br /> method 8015M; for benzene, toluene, ethylbenzene, and xylenes (BTEX) by EPA method 8021B; <br /> and for ethylene glycol and diethylene glycol by EPA method 8015M. The results are summarized <br /> below and the laboratory reports and chain of custody documentation are included in Attachment B. <br /> • Sample 1C3' — TPHg, TPHd, TPHmo, BTEX constituents, ethylene glycol, and diethylene <br /> glycol were not reported above laboratory detection limits. <br /> • Sample 3C3' — TPHg, TPHd, TPHmo, BTEX constituents, ethylene glycol, and diethylene <br /> glycol were not reported above laboratory detection limits. <br /> G:IGROUNDZEILangum EscalonlReporWSoil Removal Workplan.doc <br />
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