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Environmental Health - Public
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2900 - Site Mitigation Program
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PR0009011
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
5/19/2020 3:01:33 PM
Creation date
5/19/2020 1:47:19 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0009011
PE
2954
FACILITY_ID
FA0004080
FACILITY_NAME
NAVCOMSTA
STREET_NUMBER
305
Direction
W
STREET_NAME
FYFFE
STREET_TYPE
ST
City
STOCKTON
Zip
952035000
CURRENT_STATUS
01
SITE_LOCATION
305 W FYFFE ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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Specific Comments <br /> Comment 1 Page 3-5, Section 3.2, Determination of Removal Scope, Site SA <br /> The EE/CA should explain the significance of excavating to 10 mg/kg <br /> polychlorinated biphenyls (PCBs) and at least 10 inches of soil in the swale. <br /> Excavating to 10 mg/kg PCBs does not address the metal concentrations which <br /> need to be removed. Furthermore, soil in the Swale has not been tested for <br /> total petroleum hydrocarbons (TPH) and volatile organic compounds (VOCs), <br /> and the ground water beneath the sivale has not been tested at all. <br /> The EE/CA should explain why 170 cubic yards (cy) of soil can be excavated <br /> in the swale but only 20 cy can be excavated in the vicinity of the former drain <br /> line. The EE/CA does not state whether or not contaminated soils, if found <br /> ne_rt to sump, will be excavated after removal of the sump contents. <br /> Response: The EE/CA cites Title 40 of the Code of Federal Regulations Section 761.130 <br /> as a contaminant-specific applicable or relevant and appropriate requirement <br /> (ARAR) for PCBs. This regulation requires excavation of a minimum of 10 <br /> inches of soil at PCB spill locations, and also that PCB concentrations in soil <br /> do not exceed 10 mg/kg after the excavation is complete. The EE/CA states <br /> (in lines 1 and 5 of paragraph 2, page 3-5) that the recommended action is <br /> interim and that final cleanbp of the swale (if necessary) will be integrated <br /> with the response (if necessary) to Site 5D (line 6, paragraph 2, page 3-5). <br /> Because there are no contaminant-specific ARARs for metals and because <br /> background levels for metals are not available, the proposed action is limited <br /> to removing surficial soils. However, soil containing potentially elevated <br /> metals concentrations will be removed with the PCB-containing soil, thus the <br /> action also addresses the metals on an interim basis. <br /> The scope of the EE/CA with regard to the Swale at Site 5A includes an <br /> interim action to remove spilled PCBs and control high levels of metals (page <br /> 3-5). The presence of TPH in the swale soil will not significantly affect the <br /> ultimate disposition of Swale soils as a result of the presence or PCBs and <br /> metals. For this reason, TPH was not chosen as an analyte during the <br /> additional investigation. Because the surficial soils (0 to 0.5 foot) were <br /> sampled from the swale, it was not practical to analyze for VOCs; VOCs <br /> would not persist in the surface soil because of their tendency to evaporate <br /> and photo-degrade. Thus, samples for VOC analysis were not collected. <br /> Groundwater is monitored in well W-24, approximately 65 feet southwest of <br /> the swale. If additional monitoring wells are needed at Site 5A, they will be <br /> installed during the future remedial investigation (RI). <br /> The volume of soil (170 cy) is estimated by multiplying the swale length and <br /> width by the 10-inch excavation depth. The 20 cy estimate is based on the <br /> observed data from under the drainline (Tables 2-5 and 2-6), experience <br /> EEC.IRESPSTA:044-3321RERE I:11/15/95 1106wn 2 <br />
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