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DOE-HDBK-1129-99
addition of new streams or changes to existing streams. In addition, the regulations must be
monitored to address promulgated and proposed changes that affect current or future
characterization programs.
The Resource Conservation and Recovery Act (RCRA), an amendment to the Solid Waste
Disposal Act, was enacted in 1976 to address the management of municipal and industrial wastes.
RCRA includes a number of subtitles. Subtitle C of RCRA directs the management of hazardous
waste. This subtitle imposes administrative provisions to ensure accountability for hazardous
waste management, as well as substantive requirements designed to protect human health and
the environment from the effects of improper management of hazardous waste. Under the RCRA
implementing regulations, hazardous waste is defined as any solid waste exhibiting one or more of
the characteristics of hazardous waste -- ignitability, corrosivity, reactivity, and metal or organic
compound toxicity [40 CFR 261.20 - .24]; or is included on one of three lists of hazardous wastes
[40 CFR 261.30 - .33]. These lists include hazardous wastes generated by nonspecific (F-listed
wastes) and specific sources (K-listed wastes), in addition to commercial chemical products (P-
and U-listed wastes). RCRA was amended significantly in 1984 by the Hazardous and Solid
Waste Amendments (HSWA), which expanded the scope and requirements of RCRA. Among
other things, HSWA required EPA to evaluate all listed and characteristic hazardous wastes, and
to develop requirements (i.e., treatment standards) that must be achieved prior to land disposal of
these wastes. The implementing regulations for accomplishing this statutory requirement are
established within the Land Disposal Restrictions (LDR) program [40 CFR 268].
In conjunction with the hazardous waste and LDR-related waste determinations, additional
physical and chemical information may be required depending on the treatment or disposal options
being considered. These parameters may include, but are not limited to, the assessment of the
waste for free liquids, headspace gases, chelating agents, anions/cations, PCBs, particulate,
explosives, pyrophorics, and waste matrix composition.
8.2.1 Waste Knowledge
Waste knowledge or acceptable knowledge refers to information used to support waste
characterization activities. In recent regulatory preambles and guidance, EPA uses the terms
"waste knowledge" or "acceptable knowledge" in place of the term "process knowledge." The
terms "waste knowledge" or "acceptable knowledge" are broader terms that include process
knowledge, waste analysis data obtained from generators, and existing records of analysis, or a
combination of this information supplemented with chemical analysis. Process knowledge is the
common terminology for the RCRA regulatory language "applying knowledge of the hazard
characteristic of the waste in light of the materials or the processes used." [40 CFR 262.11(c)(2)]
EPA has defined process knowledge to include detailed information on the wastes obtained from
existing published or documented waste analysis data or studies conducted on hazardous wastes
generated by similar processes [see Joint NRC/EPA Guidance on Testing Requirements for Mixed
Radioactive and Hazardous Waste, November 20, 1997 (62 FR 62079); and Waste Analysis at
Facilities that Generate, Treat, Store, and Dispose of Hazardous Wastes: A Guidance Manual,
OSWER 9938.4-03, April 1994]. Process knowledge includes any documentation that describes or
verifies a facility's history, mission, and operations, in addition to waste stream-specific information
used to define generating process, matrix, contaminants, and physical properties. Waste-
generating facilities should maintain and utilize waste knowledge to characterize waste streams
(i.e., in lieu of sampling and analyzing the waste), whenever possible, to avoid unnecessary
exposures to radioactivity and eliminate needless or redundant waste testing. This requires the
generator to maintain auditable records that document the composition of the waste, including
waste matrix and contaminants.
94


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