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ARCHIVED REPORTS_XR0008739
Environmental Health - Public
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3500 - Local Oversight Program
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PR0545834
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ARCHIVED REPORTS_XR0008739
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Last modified
7/15/2020 10:39:34 PM
Creation date
7/15/2020 1:45:16 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0008739
RECORD_ID
PR0545834
PE
3528
FACILITY_ID
FA0005104
FACILITY_NAME
ECONO GAS
STREET_NUMBER
4325
Direction
E
STREET_NAME
WASHINGTON
STREET_TYPE
ST
City
STOCKTON
Zip
95205
APN
15733708
CURRENT_STATUS
02
SITE_LOCATION
4325 E WASHINGTON ST
P_LOCATION
99
P_DISTRICT
002
QC Status
Approved
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EHD - Public
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23 Samph <br /> During drilling all soil samples and drill cuttings were logged by a geologist using the Unified Soil <br /> Classification System In addition, all soil samples and drill cuttings were field screened for volatile <br /> organic compounds using a photoionization detector (PID) equipped Wath a 10 6 eV lamp calibrated <br /> to an isobutlyene standard These readings and any subjective evidence of petroleum hydrocarbons <br /> were recorded on the boring logs <br /> Soil samples were collected every 5 feet or at obvious changes in lithology using a split spoon <br /> sampler Soil samples were collected from the sampler in brass tubes and sealed with Teflon'tape <br /> and plastic end-caps The soil samples were labeled with the appropriate borehole location, time and <br /> date of collection,and placed in ice-cooled storage for subsequent transport and analysis at Quanterra <br /> Environmental Services Laboratory located in Santa Ana, California Chain-of-custody procedures <br /> were followed at all times Selected soil samples were analyzed using EPA Method 8015 Modified <br /> (CADHS)for TPHg,and EPA Method CADHS for benzene, toluene, ethylbenzene, and total xylene <br /> isomers (BTEX), and methyl-tert-butylether (MTBE) After sampling, each boring was backfilled <br /> to the surface with neat cement and restored to match existing conditions <br /> 24 Waste Handling <br /> During drilling operations, all augers, sampling tools, and down hole equipment was steam cleaned <br /> prior to use. All soil cuttings and rinsate water generated during drilling operations is currently stored <br /> on-site in 55-gallon drums pending evaluation options for proper disposal A composite sample was <br />. collected from the soil generated for waste profiling and analyzed for TPHg, BTEX, and MTBE <br /> Analytical results are presented m Appendix B <br /> 3.0 RESULTS <br /> 31 L1_t_b_Qloiz <br /> Soil samples collected from the borings during this investigation, consisted predominantly of sands <br /> clays, and salts In general,a sandy clay exists from near ground surface to approximately 9 feet bgs. <br /> A clayey to sandy salt exists from 9 feet bgs to approximately 30 feet bgs A sandy clay exists from <br /> 30 feet bgs to approximately 37 feet bgs Beneath the sandy clay, a sand exists from 37 feet bgs to <br /> approximately 42 feet bgs Under the sand, a gravelly sand exists from 42 feet bgs to approximately <br /> 51 feet bgs Beneath the sand, a sandy clay to clayey sand exists from 61 feet bgs to approximately <br /> 67 feet bgs From 67 feet bgs to approximately 70 feet bgs(the total sampled depth of soil boring <br /> CB-1),a sand was encountered Soil boring logs containing detailed descriptions of soil conditions <br /> encountered in each boring are included in Appendix C <br /> 32 1d <br /> Soil samples were selected on the basis of field observations and PID screening results A total of <br /> ten soil samples were analyzed for TPHg, BTEX, and MTBE. The distribution of soil sample <br /> analytical results for petroleum hydrocarbon constituents is illustrated on Figure 3 and summarized <br /> 43251NV RPT SECOR <br /> !0700-019-02 2 March 17 1997 <br />
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