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4.1.4 Physical Barriers <br /> A physical barrier controls migration of the leachate or leachate-impacted groundwater by <br /> placing a physical barrier around the downgradient edge of the plume. The technology <br /> consists of excavating a trench to a continuous, low-permeability aquitard under the <br /> property. Due to equipment limitations, maximum practical and cost-effective barrier depth <br /> is between 60 to 70 feet. The trench is typically 2.5 to 4 feet wide. After completion, the <br /> trench is backfilled with low permeable material such as a soil-bentonite slurry. If the <br /> excavated soil is not impacted then the excavated soil can be mixed with bentonite to form <br /> the slurry. The soil-bentonite slurry forms a low-permeability wall inhibiting the flow of <br /> leachate-impacted groundwater. <br /> In some applications,particularly where the solid waste has been placed below the level of <br /> the groundwater table,an upgradient barrier may be used to prevent the groundwater from <br /> contacting the waste. Alternately,either in place of, or in addition to an upgradient barrier, <br /> a downgradient barrier may be used to restrict off-site migration of impacted groundwater. <br /> Although properly designed and installed physical barriers are capable of inhibiting <br /> leachate migration, they have limited effect on groundwater movement. Additionally, <br /> unless the physical barrier completely surrounds the area of concern, it is difficult to <br /> completely intercept and contain all impacted groundwater. Therefore, physical barriers <br /> are typically used in concert with other technologies such as capping or groundwater <br /> extraction (to maintain a negative hydraulic gradient),or both. <br /> As described in Section 4.1.3, the Corral Hollow SanitaryLandfill is underlain b two <br /> Y <br /> water-bearing zones; a shallow perched zone within the Corcoran Clay and a deep <br /> regional water-bearing zone overlain by approximately 200 feet of unsaturated low <br /> permeability sediments (see Drawings 1 and 2). These sediments would restrict vertical <br /> infiltration of groundwater from the shallow perched zone. The shallow perched zone is <br /> located in the upper half of the Corcoran Clay,which is approximately 50 feet thick. <br /> A slurry wall for the purpose of containment would have to penetrate that shallow perched <br /> zone and be anchored deep in the Corcoran Clay. It is estimated that a bentonite slurry <br /> wall approximately 600 feet long and 100 feet deep would have to be constructed <br /> downgradient of MW-5 and perpendicular to the direction of groundwater flow (see <br /> Figure 4.) <br /> 4.2 Alternative Evaluation <br /> This section presents an evaluation of the alternatives. Each alternative was evaluated <br /> based on implementability,effectiveness,regulatory agency acceptance, and life cycle cost. <br /> SAC\N\PJM3M390031.9BG-94\c :1 Rev. 4 0 <br /> � 2 /9S <br /> 0939.003.19 4-4 <br />