4.2 OVERVIEW OF EVALUATION CRITERIA The evaluation criteria for Alternatives 1 through 8 are based on statutory requirements of CERCLA as amended by the Superfund Amendment Reauthorization Act (SARA), Section 121; the NCP; and the existing "Guidance for Conducting Remedial Investigations and Feasibility Studies under CERCLA" dated October 1988 (Office of Solid Waste and Emergency Response [OSWER] Directive No. 9355.3-01). The seven criteria used for evaluating alternatives are discussed below. Overall protection of human health and the environment -- This criterion describes how each alternative, as a whole, protects human health and the environment and indicates how each contaminant source is to be eliminated, reduced, or controlled. Compliance with ARARs -- This criterion evaluates each alternative's compliance with ARARs, or, if an ARAR waiver is required, how the waiver is justified. ARARs consider location-specific, chemical-specific, and cleanup action- specific concerns. Long-term effectiveness and permanence -- This criterion evaluates the effectiveness of alternatives in protecting human health and the environment after the remedial action is complete. Factors include magnitude of residual risks, adequacy of release controls, and reliability of release controls. Reduction of toxicity, mobility, or volume through treatment -- This criterion evaluates the anticipated performance of the specific treatment technologies to reduce the toxicity, mobility, or volume of contaminants. As stated in CERCLA Section 121(b)(1), "remedial actions in which treatment permanently and significantly reduces the volume, toxicity or mobility of the hazardous substances, pollutants, and contaminants is a principal element, are to be preferred over remedial actions not involving such treatment." Short-term effectiveness -- This criterion examines the effectiveness of alternatives in protecting human health and the environment during the construction and implementation period. Four factors are considered when assessing the short-term effectiveness of an alternative: protection of the community during remedial actions, protection of workers during remedial actions, environmental impacts, and time required to complete remedial action. Implementability -- This criterion evaluates the technical and administrative feasibility of each alternative and the availability of required resources. Cost -- This criterion evaluates the capital, O&M, and present worth cost of each alternative. The present worth cost is presented as the net present value. Cost estimates for the alternatives were prepared from cost information included in EPA's "Compendium of Costs of Remedial Technologies at Hazardous Waste Sites," the 1992 Means Construction Cost Data Guide, EPA's "Remedial Action at Waste Disposal Sites Handbook," estimates for similar projects, estimates from processes demonstrated under EPA's SITE program, and estimates provided by equipment manufacturers. The estimated costs are primarily based on available cost data for implementing existing, constructed treatment systems used to treat soil and sediment. Cost savings may be achieved by designing and constructing larger systems that are suited to site-specific wastes. However, little cost data is available concerning treatment of solid wastes with alternative treatment technologies. Therefore, actual costs may significantly increase based on the wastes encountered and treated. Capital and O&M cost estimates are order-of-magnitude level estimates; that is, the cost estimates have an expected accuracy of -30 to +50 percent. The estimated present worth of remedial alternatives is based on 7.5 percent discount rates (as specified in Office of Management and Budget Circular A-94) and a 30-year life. Cost tables for each alternative are presented in the text of this report. The costs in these tables are rounded to three significant figures, and the present worth costs are rounded to two significant figures. Detailed cost tables are presented in Appendix C. The two nontechnical criteria of state and community acceptance are not addressed in this FS report because the report will not be used as a decision document. Community acceptance will be addressed after public comments are received on this FS report. In the sections below, each alternative is developed and described, assessed against the seven evaluation criteria, and comparatively analyzed to assess the relative performance of each alternative with respect to these criteria.