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Environmental Health - Public
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3500 - Local Oversight Program
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PR0545144
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FIELD DOCUMENTS
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Last modified
1/9/2020 8:54:31 AM
Creation date
1/9/2020 8:41:48 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
FIELD DOCUMENTS
RECORD_ID
PR0545144
PE
3528
FACILITY_ID
FA0025676
FACILITY_NAME
CARNATION USA/CARNATION PLANT
STREET_NUMBER
969
Direction
E
STREET_NAME
FREMONT
STREET_TYPE
ST
City
STOCKTON
Zip
95202
CURRENT_STATUS
02
SITE_LOCATION
969 E FREMONT ST
QC Status
Approved
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EHD - Public
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fractions of gasoline can move in a vapor state. With the high <br /> relative porosity of the site' s :=fine-textured. soil, even with a <br /> high moisture content the volatile organics have likely moved i <br /> farther than the lead. Therefore, utilizing the presence or <br /> absence of the volatile petroleum hydrocarbons for contamination <br /> indication should be sufficiently conservative to delineate the <br /> lead contaminated zone at the site. Confirmation would be <br /> provided by the laboratory analyses, <br /> of the soil samples . <br /> Soil samples would be obtained in the following manner. <br /> Commencing at the bottom of the�foriginal excavation under the i <br /> removed tanks, camples would betaken every five feetiuntil two } <br /> consecutive samples do not have ' cations of contamination. <br /> Should the sam les continue t o with depth the <br /> last s le would be removed at ;; t 1 feet above the <br /> anticipated first ground water zone. <br /> Soil samples would be obtained by pushing a split-spoon sampler <br /> with appropriate liners below the lowest penetration of the <br /> hollow-stem flight auger. The split-spoon and liners would be <br /> prepared and handled according to a. .sampling protocol developed <br /> for the site taking into account the materials to be investigated <br /> and the materials in the sampler. The sampling protocol is <br /> included in Appendix B attached'to this report. <br /> Samples obtained from the above. program would be stored in an ice <br /> chest with non-contaminating ice (dry ice or distilled water ice j <br /> in clean polyethylene plastic) and shipped to the consulting <br /> laboratory for analysis . Chain.,of custody forms will be <br /> transmitted with the clearly labeled samples . Examples of the <br /> labels and forms are included in Appendix B. The samples will be <br /> analyzed for total petroleum hydrocarbons, total leadl,and soluble <br /> lead. ` revious analyses indicated the levels? o!' BTX and EDB arm j <br /> T below thresholds of concern, therefore there is .no apparent �^ <br /> reason to analyze }for these parameters . AO LL) l �' <br /> Contaminated drilling spoils will be- stored on-site in a = 5, � <br /> designated area for eventual disposition in accordance with an �� <br /> approved soil remedial plan. After the borings are drilled to <br /> the needed depth they will be filled: with c4ea or <br /> !a nite rout de2ending on the source and availability of <br /> native soil. If the requirements cannot be met by the native <br /> soil or local agencies prefer clean. bentonite, bentonite will be <br /> used. Based on the existing information, the local native clays <br /> are an excellent boring closureEmaterial. <br />
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