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Denmar US American Soda Ash Terminal at the Port of Stockton <br /> 19113.000.001 Work Plan for Groundwater Characterization <br /> WORK PLAN FOR GROUNDWATER CHARACTERIZATION <br /> This document presents a work plan for the planned groundwater sampling for the proposed <br /> American Soda Ash Terminal project at the Port of Stockton. The purpose of the work plan is to <br /> provide an overview of the proposed groundwater characterization program developed to meet <br /> the Notice of Intent (NOI) requirements for Central Valley Regional Water Quality Control Board <br /> (RWQCB) Order No. R5-2022-0006, Waste Discharge Requirements for Limited Threat <br /> Discharges to Surface Waters (General Order). <br /> The following sections provide descriptions of the planned field visits, explorations, and <br /> associated equipment to be used. A copy of this work plan will be available on-site for field staff <br /> to reference. <br /> PROJECT SITE AND BACKGROUND <br /> The American Soda Ash Terminal project is located on Rough and Ready Island within the Port <br /> of Stockton. Temporary dewatering and discharge of pumped groundwater will be required during <br /> construction of the below-grade dumper pit and underground utilities. The proposed dewatering <br /> area is located west of Humphreys Street and east of Burns Cutoff, as shown in Figure 1, labeled <br /> as "Limits of Excavation". The discharge point will be determined later, upon completion of <br /> analytical testing and coordination with RWQCB staff. <br /> We modeled the potential effects of the temporary dewatering in our December 3, 2021 <br /> "Preliminary Dewatering Analysis," attached. We evaluated two dewatering scenarios based on <br /> different shoring permeability options. One option is a relatively impermeable shoring, such as <br /> sheet piles or soil mix, and the other is a high-permeability shoring, such as soldier piles and <br /> lagging. Because the relatively impermeable shoring option would be dewatered from inside the <br /> excavation, the zone of influence for this option is very small (with drawdown outside the shoring <br /> only extending for a few feet). The high-permeability option would require significantly more wells <br /> and the wells would need to be outside the shoring. As such, the zone of influence for the <br /> high-permeability option is significantly greater(on the order of 700 feet from the excavation). This <br /> work plan includes groundwater characterization for either dewatering option to inform the project <br /> of any significant difference in groundwater quality based on the zone of influence created during <br /> dewatering. <br /> We will collect groundwater samples from seven locations, as shown in Figure 1. We will conduct <br /> two supplemental borings within the planned excavation footprint; these are shown at 1-S1 and <br /> 1-S2. One sample will be collected from each supplemental boring to characterize groundwater <br /> quality within the smaller zone of influence. In addition, five samples will be collected from existing <br /> wells surrounding the planned dewatering location to characterize groundwater quality within the <br /> larger zone of influence.All groundwater samples will be transported to a State-certified laboratory <br /> under documented chain-of-custody. Laboratory analysis will be performed for the applicable <br /> constituents identified in Attachment I of the General Order. Additional information about the <br /> proposed field exploration and laboratory analysis is provided below. <br /> ENGEOApril 6, 2023 <br /> Expect Excellence— <br />