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COMPLIANCE INFO_FILE 1
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COMPLIANCE INFO_FILE 1
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Last modified
2/12/2020 5:23:18 PM
Creation date
2/12/2020 3:01:34 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
COMPLIANCE INFO
FileName_PostFix
FILE 1
RECORD_ID
PR0523599
PE
2960
FACILITY_ID
FA0015929
FACILITY_NAME
PORT OF STOCKTON BLDG #16
STREET_NUMBER
305
STREET_NAME
FYFFE
STREET_TYPE
AVE
City
STOCKTON
Zip
95201
CURRENT_STATUS
01
SITE_LOCATION
305 FYFFE AVE BLDG 16
QC Status
Approved
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EHD - Public
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BUILDING 16 FORMER USTS GROUND WATER INVESTIGATION WORK PLAN <br /> PORT WEST COMPLEX,ROUGH AND READY ISLAND,PORT OF STOCKTON <br /> Based on observations to be made in the field, additional borings C15 through C19 may be <br /> advanced to assess ground water quality approximately 500 feet downgradient from the Site <br /> (Figure 18). <br /> 3.2.1 Boring Advancement <br /> The borings will be advanced using hydraulic direct push equipment to approximately 20 feet <br /> bgs, which is anticipated to intercept ground water contained within the native silts and clays. <br /> In addition, borings C1, C9, and C10 will be advanced to approximately 35 feet. All drilling <br /> equipment will be decontaminated between each sampling location. <br /> 3.2.2 Soil Sampling <br /> In the borings, soil samples will be collected continuously and described with regard to soil <br /> type, relative moisture, and color in accordance with the Unified Soil Classification System. In <br /> addition, possible volatile organic compounds emanating from the soil samples collected near <br /> the former USTS will be screened by placing the soil sample in a sealable plastic bag (e.g., zip- <br /> lock) and using a photo-ionization detector (PID) to measure the headspace in the bag. Soil <br /> samples collected from the borings are not proposed for laboratory analysis. <br /> 3.2.3 Ground Water Sampling and Analysis <br /> Grab ground water samples will be collected from two depths within each of the borings. The <br /> first sample will be collected from within the shallow sandy fill materials by stopping the <br /> boring at the approximate base of the sandy fill. The second sample will be collected between <br /> 15 feet and 20 feet bgs, from within the underlying silts and clays. In the event that shallow <br /> sandy fill materials are not encountered, the boring will simply continue to approximately 20 <br /> feet and a grab ground water sample will be collected. Deeper grab ground water samples will <br /> be collected between 30 feet and 35 feet bgs from borings C1, C9, and C10. In all cases, coarser <br /> grained sandy lenses within the silts and clays will be preferentially targeted for sampling <br /> ground water. <br /> Upon reaching the desired depth in the boring, 5 feet of slotted PVC screen will be lowered <br /> into the boring to serve as temporary well casing. Ground water grab samples will be collected <br /> within the PVC screen using a bailer constructed of Teflon, PVC, or stainless steel. The ground <br /> water samples will be gently conveyed into laboratory-supplied containers for the appropriate <br /> type of analyses. The ground water sample containers will be sealed, labeled, and placed in a <br /> cooler containing ice immediately after collection. The samples will be transport to a state- <br /> certified laboratory under standard chain-of-custody protocols. <br /> Environmental Risk Services,Corp. <br />
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