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Mr. Robert McClellon <br />March 7, 2011 <br />Page 2 <br />Environmental Protection Agency (USEPA) Subtitle D regulations and California Code of <br />Regulations (CCR) Title 27 regulations. <br />As part of the expansion, Forward will install new LFG monitoring probes which are <br />proposed to be located between the property boundary and the limit of waste in the new cell. <br />The design and specifications of the new LFG monitoring probes are in accordance with <br />applicable CCR Title 27 regulations detailed below. <br />CCR Title 27 Requirements <br />The scope and requirements for LFG monitoring and control are outlined in the CCR Title <br />27, Division 2, Chapter 3, Subchapter 4, Article 6. Section 20925 outlines the requirements <br />for the design of the monitoring probes, including the location of the probes with respect to <br />the waste limits, the spacing and depth of the probes, and their configuration relative to the <br />depth of waste. Requirements for LFG monitoring probes include: <br />• Install around the waste footprint but not within the refuse; <br />• Install at or near the disposal site permitted facility boundary; <br />• Install within 1,000 feet of nearest monitoring probe; <br />• Install adjacent to subsurface materials most conducive to gas flow; <br />• Wellbore depth equal to the maximum depth of refuse; <br />• Contain shallow (within 5-10 feet of surface), intermediate (around half the depth of <br />the refuse), and deep (at or near the depth of the waste) monitoring intervals; and <br />• Install above the permanent low seasonal water table, above and below perched <br />ground water, and place adjacent to materials which are most conducive to gas flow. <br />The new LFG monitoring probes have been designed in accordance with the above <br />requirements. There are no requirements in Article 6 pertaining to the setback of LFG <br />monitoring probes from the limit of waste. <br />The new probes are being designed similarly to other existing probes at the Landfill which <br />have been effective in detecting LFG migration. The probe design currently used at the site, <br />in many cases an approximately 50 -foot setback or less from the waste footprint, has been <br />effective in detecting LFG migration and therefore can be used as a guideline for the <br />placement of the new probes. A probe setback of 50 feet is typical at the landfills as it allows <br />for traffic flow and equipment operations between the waste limit and the monitoring probes. <br />The Landfill is located in the northern San Joaquin Valley where shallow sediment typically <br />consists of fine-grained clays and silts with interbedded coarser grained sediments deposited <br />in a meandering fluvial environment. A previous geotechnical investigation completed at the <br />Landfill (Geotechnical Investigation Report, Forward Landfill Expansion, San Joaquin <br />County, California, Geologic Associates, revised February 2008) characterized the upper 28 <br />to 40 feet of sediment as highly interbedded sandy silt, clayey silt, silt, and clay. This soil <br />matrix is underlain by a gray -brown interbedded sand, silty sand, and minor clay subunit that <br />