Hazardous waste RCRA listed

Congress, in an attempt to promote mineral development in the United States, has exempted most hazardous wastes produced at the wellsite under the Resource Conservation and Recovery Act (RCRA) Subtitle C regulations. Hazardous wastes are listed due to inherent characteristics of ... 

Pesticides are very much a part of the definition of hazardous wastes (Table 11). In fact, the toxicity characteristic of hazardous waste as defined by RCRA (referred to as extraction procedure or EP toxicity) is based on threshold concentrations of eight metals and six pesticides in an extract of the waste (Table II-A). Sixteen of the specific hazardous waste streams listed by... 

Hazardous wastes containing listed toxic substances and wastes that are reactive, ignitable, corrosive, or toxic are covered under RCRA. 

One of the critical differences between characteristic hazardous wastes and listed hazardous wastes is that, under RCRA regulations, any wastes derived from the treatment, storage, or disposal of a listed hazardous waste (e.g., treatment residues or secondary wastes from storage) are themselves regulated as listed hazardous waste. In addition, any mixture of a solid waste and a listed hazardous waste is then also designated as a listed hazardous waste. The listed hazardous waste designation applies regardless of the actual hazardous characteristics of the waste. Unlike listed hazardous wastes, wastes that exhibit one or more of the RCRA characteristics are not subject to the mixture... 

One of the important differences between characteristic hazardous wastes and listed hazardous wastes is that, under RCRA regulations, any wastes derived from the treatment. 

In addition, pnrsnant to the RCRA mixture and derived-from rules O CFR 261.3(a)(2)(iv) and 40 CFR 261.3(c)(2)(i), respectively—wastes that are mixed with listed hazardous waste or that are derived from the treatment, storage, or disposal of listed hazardous waste (e.g., treatment residues) are themselves regulated as listed hazardous waste. RCRA, however, provides an exclusion mechanism, known as a delisting petition, that generators may use to demonstrate that a listed hazardous waste, including mixture and derived-from waste, is not hazardous (40 CFR 260.22). Delistings are risk-based exclusions that... 

As with aU other hazardous substances, RCRA listed hazardous wastes (i.e., F, K, P, and U) and characteristic wastes are reportable if the release equals or exceeds the designated RQ. The release of a material that exhibits one or more characteristics of hazardous... 

Hazardous Wastes The U.S. EPA has defined hazardous waste in RCRA regulations, CFR Parts 260 and 261. A waste may be hazardous if it exhibits one or more of the following characteristics (1) ignitability, (2) corrosivity, (3) reactivity, and (4) toxicity. A detailed definition of these terms was first published in the Federal Register on May 19, 1980, pages 33, 121-122. A waste may be hazardous if listed in Appendix Wll. 

Notification to the NRC is required for releases equal to or greater than the reportable quantity of a RCRA hazardous waste. If the waste also is on the CERCLA list, that reportable quantity applies. If not, the reportable quantity is 100 pounds if the waste is ignitable, corrosive, reactive, or toxic. 

Mineral Oil Hydraulic Fluids. Disposal of used mineral oil hydraulic fluids is regulated as used oil under the Solid Waste Disposal Act as amended by the Resource Conservation and Recovery Act (RCRA) and as amended by the Used Oil Recycling Act (42 U.S.C. 6901, 6905, 6935, 6937-6939, and 6074, see 40 CFR parts 260, 261, 266, 271, and 279). Used mineral oil hydraulic fluids to be recycled are not listed as hazardous wastes and can be burned for energy recovery or recycled. In general, the newer mineral oil hydraulic fluids (including water-in-oil emulsion fluids) do not contain known chemicals or other materials that are listed in 40 CFR 261 (RCRA) and can be burned for energy recovery or recycled. However, this may not apply to some of the older hydraulic fluids, particularly those containing PCBs. 

Hazardous wastes 7 RCRA-listed wastes (K060, K087, K141 to K145)... 

There are seven Resource Conservation and Recovery Act (RCRA) listed hazardous wastes associated with coke making, as listed below ... 

Spent pickle liquor in the acid pickling wastewaters is listed as hazardous waste K062, regulated under RCRA, as it contains considerable residual acidity and high concentrations of dissolved iron salts.2 Exhausted pickling baths are mainly composed of nitrate (150 to 180 g/L), fluoride (60 to 80 g/L), iron (III) (30 to 45 g/L), chromium (III) (5 to 10 g/L), and nickel (II) (3 to 5 g/L). 

Production operations are subject to a number of regulations, including those imposed by the Resource Conservation and Recovery Act (RCRA),6 7 the Clean Water Act (CWA),8 and the Clean Air Act (CAA).9 A number of RCRA-listed hazardous wastes are produced during primary refining operations that require the heating of ores to remove impurities. Specific pretreatment standards under the CWA apply to the processes associated with copper and aluminum. Lastly, large amounts... 

The processes used in the primary production of lead produce several wastestreams of concern under different regulatory scenarios. The listed RCRA hazardous wastes include smelting plant wastes that are sent to surface impoundments to settle. The impoundments are used to collect solids from miscellaneous slurries, such as acid plant blowdown, slag granulation water, and plant... 

Wastes must be an RCRA hazardous waste in order to be subject to the LDR program. In other words, unless a waste meets the definition of a solid and hazardous waste, its disposal is not regulated under the LDR program. Once a generator identifies its waste as hazardous (either listed, characteristic, or both), the waste is assigned a waste code. When U.S. EPA establishes a treatment standard for the waste code, the waste will then become restricted (i.e., subject to the LDR requirements). RCRA requires that U.S. EPA establish treatment standards for hazardous wastes within six months of promulgating a new listing or characteristic. Until U.S. EPA establishes a treatment standard for a waste, this newly identified or newly listed waste (i.e., waste for which U.S. EPA is yet to establish a treatment... 

Residues from the combustion of hazardous waste are also potentially subject to RCRA regulation. If a combustion unit bums a listed hazardous waste, the ash could also be considered a listed waste via the derived-from rule. The owner and operator must also determine whether this ash exhibits any hazardous waste characteristics. The same is true if a unit bums waste that only exhibits a characteristic. Ash that exhibits a characteristic must be managed as a hazardous waste. 

The hazardous waste listings, the hazardous waste characteristics, and the mixture and derived-from rules are all essential parts of the definition of hazardous waste, but these key elements are all described in different sections of the RCRA regulations. Only one regulatory section unites all four elements to establish the formal definition of hazardous waste. This section is entitled Definition of Hazardous Waste, which states that all solid wastes exhibiting one of the four hazardous characteristics are hazardous wastes. This section also states that all solid wastes listed on one of the four hazardous waste lists are hazardous wastes. Finally, this section explains in detail the mixture and derived-from rules and the regulatory exemptions from these rules. Thus, although the section is entitled Definition of Hazardous Waste, it serves primarily as a guide to the mixture and derived-from rules. 

U.S. EPA proposed to significantly impact the RCRA hazardous waste identification process through a rulemaking effort called the Hazardous Waste Identification Rules (H WIR). The first rule, HWIR-media, was finalized on November 30,1998, and addressed contaminated media.16 The second rule, HWIR-waste, was finalized on May 16, 2001, and modified the mixture and derived-from rules, as well as the contained-in policy for listed wastes.5 Both the HWIR-media rule and the HWIR-waste rule attempt to increase flexibility in the hazardous waste identification system by providing a regulatory mechanism for certain hazardous wastes with low concentrations of hazardous constituents to exit the RCRA Subtitle C universe. 

The risk assessment has also concluded that a level of 200 mg/kg for lead in the soil will be a protective level for expected site exposures along with an excess cancer risk level for TCE-contaminated soil (56 pg/L). Based on investigations of activities at the site, the TCE-contaminated soil has not been determined to be a listed RCRA hazardous waste, as the cleaning solution records indicate the solution contained less than 10% TCE. However, the lead-contaminated soil is an RCRA hazardous waste by characteristic in this instance due to extraction procedure (EP) toxicity. None of the waste is believed to have been disposed at the site after November 19, 1980 (the effective date for most of the RCRA treatment, storage, and disposal requirements). 

The physical properties of lead and several of its compounds are listed in Table 3-2. Lead readily tarnishes in the atmosphere but is one of the most stable fabricated metals because of its corrosive resistance to air, water, and soil (Howe 1981). A waste that contains lead or lead compounds may (or may not) be characterized a hazardous waste following testing by the Toxicity Characteristic Leaching Procedure (TCLP) as prescribed by the Resource Conservation and Recovery Act (RCRA) regulations. 

EPA has used a 25,000-pound exemption in its regulations governing recordkeeping in the management of hazardous waste under the Resource Conservation and Recovery Act (RCRA). The regulations list particular wastes as "hazardous" and establish standards that the generators of such wastes must observe. 

Under the Resource Conservation and Recovery Act (RCRA), cyanide is listed as a hazardous waste when it is a discarded commercial chemical product, off-specification species, container residue, or spill residue (EPA 1980c) a waste from non-specific sources (EPA 1981c) or a waste from specific sources (EPA 1981c). 

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