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COMPLIANCE INFO_EW-5 INSTALL PERMIT PACKAGE 2/14/25
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COMPLIANCE INFO_EW-5 INSTALL PERMIT PACKAGE 2/14/25
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Last modified
7/18/2025 9:40:07 AM
Creation date
7/18/2025 8:30:50 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
COMPLIANCE INFO
FileName_PostFix
EW-5 INSTALL PERMIT PACKAGE 2/14/25
RECORD_ID
PR0440005
PE
4433 - LANDFILL DISPOSAL SITE
FACILITY_ID
FA0004516
FACILITY_NAME
FORWARD DISPOSAL SITE
STREET_NUMBER
9999
STREET_NAME
AUSTIN
STREET_TYPE
RD
City
MANTECA
Zip
95336
APN
201060013, 5
CURRENT_STATUS
Active, billable
QC Status
Approved
Scanner
SJGOV\cfield
Supplemental fields
Site Address
9999 AUSTIN RD MANTECA 95336
Tags
EHD - Public
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Mr. Brenden Kenny <br />Central Valley Regional Water Quality Control Board <br />February 1, 2023 <br />www.arcadis.com 2/6 <br />General Information <br />The expanded scope of work for the interim remedial action presented in this Second Work Plan Addendum is <br />proposed to address the requirement in the 2017 Cleanup and Abatement Order (CAO) R5-2017-0703 for an <br />interim remedial action to address the VOC plume mass beneath the site. <br />The Work Plan (Arcadis 2019) provided a summary of the geology and hydrogeology for the surrounding area <br />and presented the known VOCs impacts based on available data at that time, specifically carbon tetrachloride <br />and its degradation product chloroform in the shallow groundwater zone beneath the site. Concentrations of <br />carbon tetrachloride and chloroform in groundwater monitoring well AMW-22S, the only shallow groundwater <br />monitoring well on the site at the time, were generally increasing, and still comprise the majority of VOC mass in <br />groundwater at this location. However, shallow and intermediate wells located hydraulically upgradient and <br />downgradient of AMW-22S (AMW-13, AMW-13B, AMW-14, AMW-21, AMW-21S, AMW-23S, AMW-23M, AMW-31 <br />and AMW-31S) had not, and still have not, indicated detections of these constituents; therefore, a potential source <br />of carbon tetrachloride and chloroform appears to be present in the vicinity of AMW-22, on the site. A summary of <br />the results of the additional investigations completed in the vicinity of the site since October 2019, and the results <br />of CDCR historical as-built records review, and a geophysical utility survey on the site were presented in the <br />Revised Work Plan Addendum (Arcadis 2022b). <br />The expanded scope of work proposed in this Second Work Plan Addendum includes installation of three <br />extraction wells (EW-2, EW-3 and EW-4), four piezometers (PZ-3, PZ-4, PZ-5 and PZ-6) and three monitoring <br />wells (AMW-50, AMW-51 and AMW-52) on the CDCR property, which are presented in Figure 1.The extraction <br />wells will be screened in the intermediate water bearing zone and the monitoring wells and piezometers will be <br />screened in the shallow and intermediate zones. The rationale for the extraction locations and quantity of <br />extraction wells was presented the Technical Memorandum submitted to the RWQCB on November 4, 2022 <br />(Arcadis 2022a, Attachment 2). <br />Drilling Details <br />The expanded scope of work includes the installation of three extraction wells, four piezometers and three <br />monitoring wells (Figure 1). A State of California C-57 licensed driller will be used to advance the boring(s) and <br />construct the extraction wells, piezometers and monitoring wells. All drilling and well construction will be <br />completed in general accordance with the requirements specified in California Well Standards (Department of <br />Water Resources [DWR] Bulletins 74-81 and 74- 90), under the supervision of a California Professional Geologist. <br />The groundwater extraction wells, piezometers and monitoring wells will be advanced using the appropriate <br />drilling technology for the depth and diameter of installation, lithology and required well design (likely either hollow <br />stem auger, sonic or air rotary drilling techniques). The borehole diameter will be at least 2 inches larger than the <br />final outside casing diameter, installed to approximately 75 to 95 feet below ground surface (feet bgs) in the <br />shallow zone and/or approximately 100-120 feet bgs to target the intermediate zone. The targeted drilling depth <br />may be modified in the field based on the soil conditions encountered during drilling. Arcadis field personnel will <br />describe the soil using the Unified Soil Classification System (USCS) and identify potential production intervals <br />and confining layers/aquitards. Continuous soil sampling will be conducted from the water table down to the target <br />depth. <br />Soil sampling equipment will be decontaminated between each sample collected and drilling (rods and/or auger <br />flights) and sampling equipment will be decontaminated between each borehole advanced . Decontamination will
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