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J.4.2 Corrective Action Management Units <br /> EPA recently amended the regulations for RCRA facilities to allow more flexibility in treatment of <br /> waste generated during corrective actions (58 FR 8658, February 16, 1993). These regulations allow the <br /> EPA Regional Administrator to designate Corrective Action Management Units (CAMUs) at a RCRA <br /> facility for treatment of remediation wastes; however, the regulations specifically exclude using CAMUs to <br /> treat normal 'as-generated'wastes. Although these regulations were developed specifically for <br /> corrective actions at RCRA hazardous waste facilities,the regulations also may be applied as ARARs to <br /> CERCLA sites, particularly where CERCLA remediation Involves management of RCRA hazardous <br /> wastes. In the past,wastes that were removed from the ground (e.g., excavation of contaminated soils) <br /> were required to comply with the treatment standards established under the LDR. An important <br /> provision of the new regulations is the specification in 40 CFR 264.552(a)(1) and (2) that: <br /> I 1. Placement of remediation wastes into or within a CAMU does not constitute land disposal <br /> of hazardous wastes <br /> 2. Consolidation or placement of remediation wastes into or within a CAMU does not <br /> constitute creation of a unit subject to MTRs (minimum technology requirements) <br /> As a result, an area or several areas at a RCRA facility (or CERCLA site) can be designated as a <br /> CAMU and the wastes can be removed from the ground,treated, and replaced within the boundaries of <br /> that CAMU without being required to comply with the LDR treatment standards. EPA's goal in issuing <br /> these regulations Is to encourage the use of more effective treatment technologies at a specific site. The <br /> regulatory impact analysis of the CAMU regulation indicated that the regulation will result in more onsite <br /> waste management, less reliance on incineration, greater reliance on innovative technologies, and a <br /> lower incidence of capping waste in place without treatment. <br /> J.5 THE CLEAN AIR ACT (CAA) OF 1990 (42 USC 7401-7642) <br /> The CAA promulgated the following standards that may or may not be ARAB at the site due to <br /> the following reasons: <br /> • National Ambient Air Quality Standards (NAAQS). NAAQS apply to total suspended <br /> particulate, sulfur dioxide, nitrogen dioxide, carbon monoxide, ozone, and lead <br /> concentrations in ambient air, and are not applicable to individual emission sources. <br /> "Prevention of significant deterioration" (PSD) regulations may apply preconstruction <br /> guidelines and monitoring to statutory sources. <br /> • New Source Performance Standards (NSPS) were developed for specific industrial <br /> categories to provide a ceiling for emissions from new sources. <br /> • National Emission Standards for Hazardous Air Pollutants (NESHAPS) regulate asbestos, <br /> beryllium, mercury, vinyl chloride, coke oven emissions, benzene, radionuclides, and <br /> Inorganic arsenic. <br /> J.6 OCCUPATIONAL SAFETY AND HEALTH ACT (OSHA) (29 USC 651-678 AND 29 CFR PARTS <br /> 1904, 1910,AND 1926) <br /> This act provides occupational safety and health requirements applicable to workers engaged in <br /> onsite field activities. The regulations are applicable to onsite work performed during implementation of <br /> a remedial action. They are applicable to nearly all remedial action options. <br /> J-3 <br />