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45 days after the end of the monitoring period. The proposed groundwater monitoring scope is provided in <br /> Table 7. Specifics about the individual water-bearing zones are described below: <br /> A-Zone. Three monitoring wells (ST/MW-1, ST/MW-14, ST/MW-15) in the A-zone currently contain <br /> benzene and/or MTBE concentrations above proposed cleanup goals. These wells will be sampled <br /> semi-annually in the first and third quarters. In addition, thirteen wells (PS/P-11, PS/P-12, PS/P-13, <br /> PS/P-21, PS/P-23, PS/MW-17, PS/MW-19, PS/WC-2SR, PS/WC-3S, PS/WC-4S, ACA-1A, ACA-2A, <br /> ACA-3AB, and ACA-4AB) will be sampled annually in the third quarter to monitor the extent of the plume. <br /> A-zone wells will be accessed for groundwater elevation data semi-annually. <br /> B-Zone. Under current and reasonably likely future land uses, there are no complete exposure pathways <br /> for groundwater from the B-zone and residual dissolved-phase concentrations in the B-zone do not present <br /> an unacceptable risk. TPHg, BTEX and MTBE concentrations are below ESLs. TPHd concentrations <br /> sporadically exceed the ESL (Table 3, Appendix E); these concentrations are most likely the result of break <br /> down products or biogenic interference. Additionally, the hydrostratigraphy of the region supports that the <br /> B-zone is not laterally continuous and is effectively monitored by the existing A-zone well network. <br /> Therefore,we propose no further monitoring of B-zone groundwater. <br /> C-Zone. Under current and reasonably likely future land uses, there are no complete exposure pathways <br /> for groundwater from the C-zone. No monitoring wells have COC concentrations that are above the <br /> proposed cleanup goals. Three C-zone wells (ACA-26, ACA-4C and ACA-5C) are proposed for annual <br /> monitoring to confirm the extent of the dissolved phase plume in the C-zone remains stable or decreasing in <br /> extent. In addition, the C-zone wells listed in Table 7 will be accessed for groundwater elevation data to <br /> document that hydraulic gradients in the C-zone remain consistent with historical groundwater flow <br /> directions. <br /> D-Zone. Under current and reasonably likely future land uses, there are no complete exposure pathways <br /> for D-zone groundwater and dissolved-phase concentrations do not present a potential unacceptable risk. <br /> Benzene and MTBE concentrations were below proposed cleanup goals and the Basin Water Quality <br /> Objectives in the most recent sampling event. Therefore,we propose no further monitoring of the D-zone. <br /> �I <br /> �1 <br /> Revised Cleanup Plan Page 22 <br /> NuStar Stockton Terminal-Stockton,California <br /> November 7,2012 <br /> 1014-12 <br />