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Last modified
2/1/2019 2:17:26 PM
Creation date
2/1/2019 2:06:47 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
FIELD DOCUMENTS
RECORD_ID
PR0506190
PE
2953
FACILITY_ID
FA0007262
FACILITY_NAME
FLORSHEIM HOMES
STREET_NUMBER
0
STREET_NAME
AUTUMN CHASE
STREET_TYPE
CIR
City
STOCKTON
Zip
95219
CURRENT_STATUS
02
SITE_LOCATION
AUTUMN CHASE CIR
P_LOCATION
01
P_DISTRICT
003
QC Status
Approved
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EHD - Public
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Florsheim Homes July 8, 1994 <br /> Mr. Robert Florsheim Page 3 of 4 <br /> ENVIROMETRIX <br /> * Sampling location, designation, and sampler <br /> Project designation and location <br /> Sampling date and time <br /> Lithologic descriptions <br /> Organic vapor readings <br /> • Sample interval <br /> Final logs for the borings and wells are presented on Plate 4. After drilling was <br /> completed, the borings were grouted to within two feet of the surface. The remaining <br /> two feet was filled with native soil as requested by Mr. Mike Inferrena an inspector <br /> with the SJCEHD who was onsite during the grouting of the borings. Soil cuttings <br /> from the borings were placed on the concrete pad adjacent to Boring B-1 and covered <br /> with plastic until the chemical analysis results are known. <br /> Soil samples were collected ahead of the drill bit using a 2-inch inside diameter (ID) <br /> modified California split-spoon sampler lined with three pre-cleaned 6-inch long <br /> stainless steel tubes. Soil samples were collected by pushing the lined split-spoon <br /> sampler 1.5 feet into the native soil using a hydraulic ram on the rig. The soil samples <br /> were screened for organic vapors in the field using an HNu photoionization detector. <br /> No organic vapors were detected. The ends of the sample tubes retained for laboratory <br /> analysis were covered with teflon tape, capped with plastic end caps, and placed in a <br /> ice chest with blue ice. All field and sampling equipment was decontaminated prior to <br /> use, and a trisodium phosphate and water solution was used to clean the split spoon <br /> samplers prior to each sampling. The groundwater sample was collected by lowering a <br /> new disposable bailer into Boring B-1 after groundwater had recharged into the boring. <br /> The sample was decanted into laboratory supplied containers. <br /> Soil samples submitted for laboratory analysis were collected in each boring just above <br /> or at the groundwater table which varied from 5.5 to 6.5 bgs. Additional soil samples <br /> were collected and placed on hold at the laboratory pending results of the initial <br /> chemical analysis. Soil and groundwater samples were submitted for laboratory <br /> analyses under Chain-of-Custody procedures to Superior Analytical Laboratories <br /> (Superior) in Martinez, California, a State-certified laboratory. Soil samples were <br /> analyzed for total petroleum hydrocarbons as diesel (TPH-D) as motor oil (TPH-MO) <br /> and gasoline (TPH-G), and benzene, toluene, ethylbenzene, and xylenes (BTEX) using <br /> State-approved methods. The chemical analysis were submitted for analysis on a rush, <br /> 24-hour turnaround basis. <br /> Results <br /> No TPH-G, TPH-D, TPH-MO, or BTEX compounds were found above detection <br /> limits in any of the soil samples or the groundwater grab sample. The chemical <br /> analysis results are presented in the laboratory reports which are attached. <br />
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