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3500 - Local Oversight Program
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PR0545731
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Last modified
6/4/2020 12:16:20 PM
Creation date
6/4/2020 11:56:55 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
WORK PLANS
RECORD_ID
PR0545731
PE
3528
FACILITY_ID
FA0004572
FACILITY_NAME
LOPEZ, ADOR
STREET_NUMBER
9015
Direction
W
STREET_NAME
WALNUT GROVE
STREET_TYPE
RD
City
THORNTON
Zip
95686
APN
00114040
CURRENT_STATUS
02
SITE_LOCATION
9015 W WALNUT GROVE RD 11
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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EHD - Public
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�Nwe %MW <br /> Work Plan for Soil Excavation/Additional Assessment 3 <br /> Barbara Drake, 26485 North Thornton Rd.,Thornton,CA October 6, 1994 <br /> TASK a: SOIL AND GROUNDWATER SAMPLING <br /> Upon completion of excavation, Groundwater Technology will supervise the coring of five soil <br /> borings at the approximate locations shown on Figure 2 using a hydraulically driven (Enviro-Care TM) <br /> soil coring device. The position of the borings may be adjusted once the groundwater gradient is <br /> determined. The borings will be 2.5 Inches in diameter and cored to a depth of approximately 13-16 <br /> feet below ground surface (BGS), approximately 2-5 feet below the water table to accommodate <br /> temporary groundwater monitoring well installation. <br /> Soil samples will be collected continuously from each soil boring using a sample barrel lined with <br /> 1.75-inch diameter by 6-inch long stainless steel sampling tubes. The sample barrel is retrieved from <br /> the outer drive casing every three feet. Sampling equipment will be cleaned between each sampling <br /> interval. The 5 and 10 feet BGS sample tube from each continuously cored section will be sealed <br /> and placed on Ice in an insulated container pending delivery to GTEL Environmental Laboratories in <br /> Concord, California. Soil retained in the other tubes will be extruded and visually examined for <br /> evidence of hydrocarbon impact and lithologic description. Soil will be screened for hydrocarbon <br /> vapors using a photo-ionization detector (PID). <br /> Upon completion of the borings to the desired depth (approximately 2-5 feet below the water table), <br /> the drive casing will be pulled up 2-5 feet from the bottom of the borehole to allow groundwater to <br /> flow into the boring and to allow construction of temporary groundwater monitoring wells. The <br /> temporary groundwater monitoring wells will be constructed of 1-inch diameter schedule 40 <br /> polyvinylchloride (PVC) well casing and 0.010-inch slot well screen. Well screen will be installed 1-2 <br /> feet above and 2-4 feet below the water table at each location. The wells will be sampled using a <br /> 3/4 inch teflon bailer. Samples will be decanted to the appropriate sampling containers and placed <br /> on ice in an insulated container pending delivery to GTEL Environmental Laboratories In Concord, <br /> California. Upon completion of sampling, each borehole will be backfilled with a mixture of Type II <br /> cement and bentonite. The grout will be tremied through a pipe positioned at the bottom of the <br /> borehole prior to withdrawal of the outer drive-casing. The extremely small volume (estimated at <br /> less than 2 cubic feet) of soil cuttings generated during the sampling process will be combined with <br /> soil from the excavation in the main stockpile. Water generated during cleaning of the coring and <br /> sampling equipment will be temporarily stored on site in a Department of Transportation-approved <br /> 55-gallon drum. <br /> S Sol T - - <br /> 5z o <br /> 0053SGA.WKP(MI5C-15) <br /> LU GROUNDWATER <br /> ���:TECHNOLOGY <br />
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