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WORK PLANS_CASE 1
Environmental Health - Public
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WORK PLANS_CASE 1
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Last modified
5/19/2021 4:33:02 PM
Creation date
5/19/2021 4:04:23 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
FileName_PostFix
CASE 1
RECORD_ID
PR0508042
PE
2960
FACILITY_ID
FA0005316
FACILITY_NAME
U S CAN COMPANY
STREET_NUMBER
35275
Direction
S
STREET_NAME
WELTY
STREET_TYPE
RD
City
VERNALIS
Zip
95385
APN
25518009
CURRENT_STATUS
01
SITE_LOCATION
35275 S WELTY RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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Ms. Penny Fottrell GEOMATRIX <br /> Chevron Environmental Management Company <br /> February 11, 2003 <br /> Page 3 <br /> Caltrans's right-of-way. The borings will be advanced and using a sonic rig, and the soil and <br /> grab groundwater samples will be collected by continuous coring and discrete-depth sampling, <br /> respectively. <br /> SOIL BORING AND SAMPLING ACTIVITIES <br /> It is anticipated that each boring will be advanced to 90 feet bgs, the depth at which previous <br /> on-site borings were drilled to obtain soil samples without petroleum constituent detections. <br /> Geomatrix proposes to collect grab groundwater samples from each of the two borings, <br /> GMX-10 and GMX-11, at sample intervals between 36 and 40 feet bgs and 76 to 80 feet bgs, <br /> where petroleum constituent affected soil was identified on-site. Groundwater samples will <br /> be collected by advancing a hydropunch tool through the center of the sonic drill casing ahead <br /> of the drilling apparatus, exposing a four foot screen, then using a disposable bailer to collect <br /> a sample. The sample will be decanted into 1-liter amber bottles and 40 milliliter acidified <br /> volatile organic analysis vials provided by the laboratory. Samples will be labeled, stored in <br /> ice-filled coolers, and delivered to a state-certified analytical laboratory under Geomatrix <br /> chain-of-custody procedures. <br /> A soil sample will be collected for laboratory analyses from each boring from impacted soil <br /> within the vadose zone, if observed. If no petroleum-impacted soil is observed in the vadose <br /> zone, then a soil sample will be collected from directly above the water table. Another soil <br /> sample will be collected from the terminus of each boring for laboratory analyses to confirm <br /> the vertical extent of affected soil (i.e., the sample will be collected from a depth where field <br /> observations/measurements do not indicate the presence of petroleum constituents). Soil <br /> samples will be collected by pressing brass sleeves (labeled and sealed with Teflon sheets, end <br /> caps, and tape) into the continuous soil core, stored in ice-filled coolers, and delivered to a <br /> state-certified analytical laboratory under Geomatrix chain-of-custody procedures. Soil bor- <br /> ings will be logged using the Unified Soil Classification System (USCS) as presented in the <br /> American Society of Testing and Materials(ASTM) Standard D2488-90. <br /> Following sample collection, the borings will be backfilled with grout in accordance with the <br /> San Joaquin County requirements. <br /> ANALYTICAL METHODS <br /> Groundwater samples will be submitted for analysis of TPHg2 using Environmental Protection <br /> Agency(EPA) Method 8015 Modified, benzene, toluene, ethylbenzene, and xylenes (BTEX) <br /> using EPA Method 8021, polynuclear aromatic hydrocarbons (PAHs) using EPA Method <br /> 8270 SIM, and TPHd using EPA Method 8015 Modified. The laboratory will perform the <br /> Z The revised CTA recommends sampling for TPHg in groundwater only if site history indicates the presence of <br /> gasoline range hydrocarbons. The high concentration of TPHg relative to TPHd in the previously collected <br /> sample from MW-1 indicates that gasoline range hydrocarbons may be present. <br />
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