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CORRESPONDENCE_2003-2005
EnvironmentalHealth
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PR0504907
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CORRESPONDENCE_2003-2005
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Last modified
4/3/2023 2:43:18 PM
Creation date
8/24/2022 11:46:57 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
CORRESPONDENCE
FileName_PostFix
2003-2005
RECORD_ID
PR0504907
PE
4430
FACILITY_ID
FA0006398
FACILITY_NAME
SNYDERS SANITARY
STREET_NUMBER
23023
Direction
S
STREET_NAME
SANTA FE
STREET_TYPE
RD
City
ESCALON
Zip
95320
CURRENT_STATUS
01
SITE_LOCATION
23023 S SANTA FE RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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SJGOV\cfield
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EHD - Public
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Mr. Robert McClellon <br /> July 1, 2004 <br /> Page 3 of 5 <br /> will be placed near the southern boundary of the property. The estimated boring locations are <br /> shown on Figure 4. <br /> Drilling Methods <br /> The borings will be advanced to a depth of approximately 30 feet bgs or until shallow groundwater <br /> is encountered. A drilling company licensed in the State of California will advance the borings <br /> using a truck mounted Geoprobe direct push drilling rig (Fisch Environmental, C57-683865). Soil <br /> samples will be collected for logging and identification purposes at 5-foot depth intervals. Samples <br /> will be collected using a 2-inch diameter core sampler lined with clear acetate sleeves. A portion of <br /> a soil sample selected for laboratory analyses will be immediately capped and preserved in an iced <br /> cooler at a temperature of approximately 4° Centigrade. No cuttings requiring disposal will be <br /> produced using the direct push drilling method. Borings will be backfilled to the ground surface <br /> with neat cement grout. <br /> We expect to submit soil samples collected from each boring at depths of approximately 10 and 20 <br /> feet bgs to a State-certified laboratory for analysis of total petroleum hydrocarbons as oil (TPHo) <br /> using EPA method 8015 modified, CAM17 metals, and soluble lead. <br /> In addition, one discrete groundwater sample will also be collected from each boring and analyzed <br /> for the constituents listed above. The groundwater samples will also be analyzed for the presence of <br /> volatile organic constituents (VOCs) using EPA 8260. Groundwater samples will be collected <br /> through a sampler driven the to the desired depth and retracted to expose the screen to the <br /> formation, or through a temporary PVC casing installed in the borehole. The sample will be <br /> collected using a length of polytetrafloroethylene (PTFE) tubing equipped with a stainless steel <br /> bottom check valve. The tubing will be inserted into the probe rods/temporary casing and pushed to <br /> the screened interval at the desired depth. The groundwater sample will be brought to the surface by <br /> gripping the top of the tubing and rapidly moving the tubing up and down creating a positive <br /> displacement effect, thereby forcing the water sample to the surface where it will be collected <br /> directly into the sample containers. <br /> All sampling and drilling equipment will be washed thoroughly with laboratory-grade detergent and <br /> water between uses to minimize the potential for cross contamination. <br /> General Site Safety Practices <br /> The CIWMB previously identified a number of potential chemical and physical hazards that may be <br /> encountered at the site. A summary of potential hazards at the site is presented below. <br /> Potential Chemical Hazards <br /> Heavy Metals <br /> Burn ash sample analysis obtained from previous waste characterization investigations from other <br /> sites indicate that non-hazardous household or municipal waste contains various heavy metals. Test <br /> G:\GROUNDZE\Palomino\wpjorings.doc <br />
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