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ARCHIVED REPORTS_XR0011006
Environmental Health - Public
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3500 - Local Oversight Program
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PR0545039
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ARCHIVED REPORTS_XR0011006
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Last modified
12/10/2019 2:06:50 PM
Creation date
12/10/2019 11:26:25 AM
Metadata
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Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0011006
RECORD_ID
PR0545039
PE
3528
FACILITY_ID
FA0010186
FACILITY_NAME
DEL MONTE FOODS PLNT #33 - DISCO WH
STREET_NUMBER
110
Direction
N
STREET_NAME
FILBERT
STREET_TYPE
ST
City
STOCKTON
Zip
95205
APN
15702009
CURRENT_STATUS
02
SITE_LOCATION
110 N FILBERT ST
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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The aquifer test will include a step-drawdown test and a constant rate discharge test. The step- <br /> drawdown test will be conducted to determine the optimal pumping rate for the constant discharge test. <br /> Prior to the step-drawdown test,water levels will be measured continuously for one to three days using <br /> downhole pressure transducers and a data logger to provide an indication of short term variations in <br /> water levels. After the step-drawdown test and prior to starting the constant rate test,the water levels <br /> will be allowed to recover to 95 percent of initial static water levels.Water level measurements from the <br /> pumped well and select observation wells will be recorded.It is anticipated that all water pumped during <br /> the pumping test will need to be temporarily stored onsite.The duration of the pumping test will be <br /> dependent upon the yield of the well and storage capacity for the pumped water. Pumping test data will <br /> be analyzed by the appropriate methods,such as Theis,Cooper Jacob,and Neuman methods. <br /> All water pumped from the extraction well during the aquifer pumping tests will be managed according <br /> to federal,state,and local regulations. <br /> 3.3 Equipment Decontamination <br /> At each drilling location,an area will be established for equipment decontamination. All CPT drill rods, <br /> drilling equipment will be steam cleaned before use,and between each soil boring. All groundwater and <br /> soil sampling equipment will be washed with Alconox soap and triple rinsed with distilled water. <br /> 3.4 Waste Characterization. and Disposal Plan <br /> Three types of waste will be generated during the activities described in this work plan: <br /> I • Rinse water from decontamination of equipment <br /> • Water from well development. <br /> • Soil cuttings and drilling fluids from mud rotary drilling(CPT logging/boring does not generate drill <br /> cuttings) <br /> Suits/protective clothing <br /> r <br /> All wastes will be temporarily stored onsite in 55-gallon drums,polyethylene storage tank(s)or roll-off <br /> bins. All containers will be labeled with information indicating the owner and source of the waste, and <br /> date of generation. For purposes of waste characterization,groundwater and soil samples will be collected <br /> j at a frequency defined by the disposal facility and analyzed for TPH-gas and BTEX by EPA Method <br /> 8015/8020, TTLC lead,and oxygenates,including 1,2-Dichloroethane (1,2-DCA), 1,2-Dibromoethane <br /> (EDB),and tert Butanol(TBA),by EPA Method 8260,in a state-certified laboratory. <br /> All hazardous wastes will be disposed of within 90 days of their collection. <br /> If prior approval is received from the local POTW,waste water may be disposed of directly to the local <br /> sanitary sewer system. All wastes will ultimately be managed according to federal,state,and local <br /> regulations. <br /> i <br /> { <br /> f <br /> i <br /> CATEMP\WaRKPLA _DGk1.DOC g <br />
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