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ARCHIVED REPORTS_XR0010848
Environmental Health - Public
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2900 - Site Mitigation Program
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PR0541431
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ARCHIVED REPORTS_XR0010848
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Last modified
12/10/2019 9:34:19 AM
Creation date
12/10/2019 9:16:14 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0010848
RECORD_ID
PR0541431
PE
2953
FACILITY_ID
FA0023745
FACILITY_NAME
DEBOER TRUCKING
STREET_NUMBER
201
Direction
W
STREET_NAME
FIFTH
STREET_TYPE
ST
City
RIPON
Zip
95366
APN
25935013
CURRENT_STATUS
01
SITE_LOCATION
201 W FIFTH ST
P_LOCATION
05
QC Status
Approved
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EHD - Public
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W� itDeBoer Truck Lines, Inc. <br /> 201 West Sth Street, Ripon, California <br /> Phase I Report of Findings September.9, 199„A <br /> � Page: ;4 <br /> Soil samples collected for analysis were analyzed using EPA method 3550ALUFT for <br /> 11 diesel range petroleum hydrocarbons and EPA method 8020 for BTX&E compounds. <br /> �- The minimum detection limits used for each analyte were .005 mg/kg for BTX&E anti <br /> 5.0 mg/kg for diesel. Analyses were conducted by GeoAnalytical Laboratories r Inc. a State-certified lab in Modesto, California. ' U <br /> ii <br /> 3.5 Groundwater Sampling <br /> A travel blank provided by the laboratory accompanied the sample vials from the time <br /> they are picked up from the lab to the time they are delivered to the lab. This travel' <br /> blank was listed on the Chain of Custody but will be analyzed only if all samples; <br /> contain the same contaminants. <br /> ,i <br /> A11 sampling-equipment including the pump, bailer, and cables, used by sampling;; <br /> personneI, were disassembled, if appropriate, and steam-cleaned prior to <br /> commencement of sampling. These procedures were also followed between each well,? <br /> sampling point, and at the end of the sampling day. De-ionized or organic-free water p <br /> (also provided by the laboratory)was then introduced into the pump or bailer as a final <br /> stage of cleaning. This water was then pumped or gently poured into sample vials to!, <br /> be used as pump or bailer blanks. These blanks were tested only iftheir corresponding <br /> " -' samples were found to contain contaminants. <br /> u <br /> Immediately prior to sampling, water levels and well depth measurements were !; <br /> recorded in all wells at the site. Each well was evacuated using either a stainless steel <br /> bladder pump, which does not introduce air into the water column, or a;Teflon bailer. <br /> The pI-L temperature, and electrical conductivity of the water was monitored with <br /> instruments calibrated to known standards as the wells were evacuated. These <br /> parameters are noted on field logs (Table 4, Appendix D). At least 5 well volumes II <br /> were evacuated from each well, or more, as necessary, until the above parameters had <br /> stabilized. The wells, or other sampling points, were sampled in order of the least to <br /> the most contaminated, as best known or estimated. The samples were pumped from a !� <br /> stainless steel bladder pump or carefully poured from a Teflon bailer into clean glass <br /> vials with-Teflon-lined screw caps and half gallon plastic containers provided by the <br /> laboratory. Care was taken to ensure that no air space exists in the vials by inverting to <br /> check for bubbles and re-sampling if necessary. <br /> The samples were analyzed or extracted within 14 days according to their EPA <br /> methods, Water samples collected for analysis were analyzed by EPA method 602 for <br /> BTX&E compounds and method 3510 for diesel range hydrocarbons. The minimum <br /> detection limits used for each analyte were 0.5 pg/kg for BTX&E and 0.5 mg/kg for <br /> diesel. Analysis were conducted by GeoAnalyticai Laboratories, Inc., a State-certified <br /> lab in Modesto, California. <br /> 4 <br />' ii <br />
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