Hazardous Waste Characteristics
A User-Friendly Reference Document
October 2009
1
Table of Contents
Introduction..................................................................................................................................... 3
Overview of the Hazardous Waste Identification Process .......................................................... 5
Characteristic Hazardous Wastes ................................................................................................ 5
Summary Chart............................................................................................................................ 7
General Hazardous Waste Resources.......................................................................................... 8
Regulations for the Identification of Hazardous Waste............................................................... 9
General Resources for Hazardous Waste Characteristics.......................................................... 12
Ignitability..................................................................................................................................... 12
Regulations for Ignitable Liquids.............................................................................................. 13
Regulations for Ignitable Solids................................................................................................ 14
Regulations for Ignitable Compressed Gas............................................................................... 14
Related Resources for Ignitable Compressed Gas..................................................................... 15
Regulations for Oxidizers.......................................................................................................... 15
Regulations for the Hazardous Waste Number for Ignitability................................................. 16
General Resources for the Ignitability Characteristic................................................................ 17
Corrosivity .................................................................................................................................... 18
Regulations for Aqueous Solutions........................................................................................... 18
Regulations for Steel Corrosivity.............................................................................................. 19
Regulations for the Hazardous Waste Number for Corrosivity ................................................ 19
General Resources for the Corrosivity Characteristic............................................................... 20
Reactivity...................................................................................................................................... 20
Regulations for Reactivity......................................................................................................... 20
Regulations for Reactivity with Water...................................................................................... 21
Regulations for Cyanide/Sulfide Reactivity.............................................................................. 21
Regulations for Explosives........................................................................................................ 21
Regulations for the Hazardous Waste Number for Reactivity.................................................. 22
General Resources for the Reactivity Characteristic ………………………………………….24
Toxicity......................................................................................................................................... 24
Regulations for Toxicity............................................................................................................ 24
General Resources for the Toxicity Characteristic.................................................................... 26
2
Introduction
This document describes the Environmental Protection Agency’s (EPA’s) hazardous
waste characteristics regulations under the authority of the Resource Conservation and Recovery
Act (RCRA) Subtitle C
1
and includes hyperlinks to information that EPA has generated over the
years to explain the characteristics regulations. The objective of this document is to consolidate
the information on characteristics regulations to assist Environmental Protection Agency (EPA)
staff, state staff, industrial facilities that generate and manage hazardous wastes, and the public to
understand the current RCRA hazardous waste characteristics regulations. The criteria for
identifying the characteristics of hazardous wastes are located in Title 40 of the Code of Federal
Regulations (CFR) at Part 261. Please note that this reference document is designed to be web-
based, so the usefulness of the document is maximized when it is viewed on a computer that is
connected to the internet.
This document is only a reference document and is not to be used as a substitute for the
CFR itself or the requirements contained in the CFR. This document is also not a rulemaking in
any way. Additionally, this reference document presents only the federal requirements for
hazardous waste characteristics. Most states are authorized to manage their hazardous waste
management regulatory program. Therefore, states may have their own set of regulations that
apply in lieu of federal regulations, and while most state hazardous waste regulations are based
on the federal requirements, some states have developed regulations that are more stringent than
the federal program. We direct you to the following website to determine if the state regulatory
program is different from the federal program: http://www.epa.gov/epawaste/wyl/stateprograms.htm
This document is organized by hazardous waste characteristic (i.e., ignitable, corrosive,
reactive and toxic), in a manner similar to the way the identification of hazardous waste
regulations are presented in Title 40 of the Code of Federal Regulations (CFR) at Part 261.
Therefore, following an overview of the hazardous waste characteristics regulations, this
document will present the definition of hazardous waste, criteria for identifying hazardous waste,
and the definitions of each of the four characteristics of hazardous waste. Background
information and relevant resources are also provided throughout this document.
To help stakeholders better understand specific requirements, we also have provided,
where applicable, hyperlinks to Federal Register notices, frequently asked questions (FAQs),
letters, and memoranda issued by EPA, as well as guidance and other relevant documents
developed by EPA that provide further clarification of the hazardous waste characteristic
regulations. We have attempted to identify the relevant related FAQs, letters, memoranda, etc.
on a particular subject (miscellaneous resources can also be found in this document). However,
please note that it is possible that EPA could have inadvertently overlooked a relevant document
and did not include it in this reference document. Therefore, we cannot guarantee that we
captured every relevant document in each and every instance. Additionally, once a user has
navigated to the characteristics regulation of interest, we have provided hyperlinks to the e-CFR
website when the characteristics regulations cross-reference themselves or other regulations.
1
Subtitle C of RCRA has been codified in the United States Code (U.S.C.) as the Solid Waste Disposal Act
(SDWA), Subchapter III (Hazardous Waste Management), 42 U.S.C. §§ 6921 through 6939e
3
Because regulations are promulgated throughout the year, EPA intends to update this
reference document periodically to remain up-to-date with the hazardous waste regulatory
requirements. However, as noted previously, this web-based reference document is not a
substitute for the CFR itself or the requirements in the CFR. Additionally, the Government
Printing Office frequently updates the e-CFR website to which the document is linked. The
hyperlinks included in this document for Federal Register notices published prior to October
1994 are from HeinOnline and are only available only by subscription to HeinOnline. By
including this material, EPA does not endorse HeinOnline.
This reference document assumes that a solid waste has been generated. Therefore, we
have not included the applicable regulatory citations for determining if a solid waste (See 40
CFR 261.2) has been generated. Similarly, we have not included the regulatory citations for
specific exclusions from either the definition of solid waste and definition of hazardous waste
found in 40 CFR 261.4, or the requirements for recyclable materials found in 40 CFR 261.6.
Similar documents have been prepared compiling regulations applicable to generators of
hazardous waste, “Hazardous Waste Generator Regulations: A User-Friendly Reference
Document, May 2007,” and the hazardous waste listings regulations, “Hazardous Waste Listings:
A User-Friendly Reference Document, Draft, March 2008.” Documents for Exclusions from the
Definition of Solid Waste have also been developed, “Definition of Solid Waste Compendium -
Volume A: Exclusions” and “Identification and Listing of Hazardous Waste 40 CFR § 261.4(b):
Exclusions: Solid Wastes Which are not Hazardous Wastes.” A collection of written materials
about specific issues related to the definition of solid waste is available, “DSW Compendium.”
This document was developed by the Materials Recovery and Waste Management Division in
the Office of Resource Conservation and Recovery (formerly Office of Solid Waste). (Name
change effective as per 74 FR 30228, June 25, 2009). Please direct any questions concerning
this document to: helm[email protected].
How to navigate this document
This document is navigable in several ways. First, generators can use the Summary
Table to link directly to the regulatory citation of interest in the
Government Printing Office’s
Electronic Code of Federal Register website (e-CFR) by left-clicking the mouse on
the hyperlinks in the table. Clicking on the hyperlink will open the e-CFR in a new web-browser
window, so the original document will also remain open. Secondly, users can take advantage of
the Table of Contents (page 2 of the document) or the bookmarks (located on the left-hand side
of the screen) to navigate through the body of the document. The Table of Contents and
bookmarks are organized by hazardous waste characteristic. Users can navigate the document by
clicking the left side of the mouse on the link of interest in the Table of Contents and bookmarks.
4
Overview of the Hazardous Waste Identification Process
EPA's regulations establish two ways of identifying solid wastes as hazardous under the
Resource Conservation and Recovery Act RCRA. A waste may be considered hazardous if it
exhibits certain hazardous properties (“characteristics”) or if it is included on a specific list of
wastes EPA has determined are hazardous (“listing” a waste as hazardous) because we found
them to pose substantial present or potential hazards to human health or the environment. EPA's
regulations in the Code of Federal Regulations (40 CFR) define four hazardous waste
characteristic properties: ignitability, corrosivity, reactivity, or toxicity (see 40 CFR 261.21-
261.24). This document presents the regulations that will assist in identifying the characteristics
of hazardous waste in §§
261.31 through 261.33. Since EPA has developed a separate document
for listed wastes, only characteristic wastes will be discussed in this document.
Characteristic Hazardous Wastes
A RCRA characteristic hazardous waste is a solid waste that exhibits at least one of four
characteristics defined in 40 CFR Part 261 subpart C — ignitability (D001), corrosivity (D002),
reactivity (D003), and toxicity (D004 - D043).
Ignitability– Ignitable wastes can create fires under certain conditions, are spontaneously
combustible, or have a flash point less than 60 °C (140 °F). Examples include waste oils
and used solvents. For more details, see 40 CFR §261.21. Test methods that may be
used to determine ignitability include the Pensky-Martens Closed-Cup Method for
Determining Ignitability (Method 1010A)(PDF)(1 pg, 19K), the Setaflash Closed-Cup
Method for Determining Ignitability (Method 1020B)(PDF) (1 pg, 17K), the Ignitability
of Solids (Method 1030) (PDF)(13 pp, 116K), Test Method for Oxidizing Solids (Method
1040)(PDF) (17 pp, 207K), and the Test Method to Determine Substances Likely to
Spontaneously Combust (Method 1050) (PDF)(20 pp, 611K).
Corrosivity – Corrosive wastes are acids or bases (pH less than or equal to 2, or greater
than or equal to 12.5) and/or are capable of corroding metal containers, such as storage
tanks, drums, and barrels. Battery acid is an example. For more details, see 40 CFR
§261.22. The test method that may be used to determine the ability of a waste to corrode
steel is the Corrosivity Towards Steel (Method 1110A)(PDF)(6 pp, 37K). To measure
pH electrometrically, see Method 9040C (PDF)(5 pp, 25K).
Reactivity – Reactive wastes are unstable under "normal" conditions. They can cause
explosions, undergo violent reactions, generate toxic fumes, gases, or vapors or explosive
mixtures when heated, compressed, or mixed with water. Examples include lithium-
sulfur batteries and explosives. For more details, see
40 CFR §261.23 . There are
currently no test methods available.
Toxicity – Toxic wastes are harmful or fatal when ingested or absorbed (e.g., containing
mercury, lead, etc.). When toxic wastes are land disposed, contaminated liquid may
leach from the waste and pollute ground water. Toxicity is defined through a laboratory
5
procedure called the Toxicity Characteristic Leaching Procedure (TCLP) (Method
1311)(PDF)(35 pp, 288K). The TCLP helps identify wastes likely to leach
concentrations of contaminants that may be harmful to human health or the environment.
For more details, see 40 CFR §261.24.
6
Summary Chart
Links to specific sections of the CFR Citations for the Characteristics of
Hazardous Waste
Title Section
40 CFR 261.3
Definition of Hazardous Waste -
General
Criteria for Identifying Characteristics
of Hazardous Waste
40 CFR 261.10
Characteristics of Hazardous Waste -
General
40 CFR 261.20
Characteristics of Ignitability
40 CFR 261.21
Characteristics of Corrosivity
40 CFR 261.22
40 CFR 261.23
Characteristics of Reactivity
40 CFR 261.24
Toxicity Characteristic
Hazardous waste determination 40 CFR 262.11
7
General Hazardous Waste Resources
Electronic Code of Federal Regulations
e-CFR: Title 40-Protection of Environment (Parts 260-265)
Hazardous waste web page on the EPA website
http://www.epa.gov/epawaste/hazard/index.htm
RCRA training modules
http://www.epa.gov/osw/inforesources/pubs/hotline/rmods.htm
Training Document on Hazardous Waste Identification
http://www.epa.gov/waste/inforesources/pubs/training/hwid05.pdf
General Questions on Hazardous Waste and Characteristics
What is a RCRA hazardous waste?
Requirements for Generators of Hazardous Waste
http://www.epa.gov/epawaste/hazard/generation/index.htm
Website for RCRA Frequent Questions Database
http://waste.custhelp.com/cgi-bin/waste.cfg/php/enduser/std_alp.php
Environmental Justice
Addressing Environmental Justice Issues In RCRA Programs
Methods for Determining Characteristics of Hazardous Waste, SW-846, Chapter 8
Important Federal Register Notices for Characteristic Hazardous Waste
Proposed Rule – Hazardous Waste Guidelines and Regulations
43 FR 58946, December 18, 1978
Final Rule and Interim Final Rule - Hazardous Waste Management System: General
45 FR 33066, May 19, 1980
Petroleum Refining Process Waste - Notice of Data Availability
68 FR 59935, October 20, 2003
8
Regulations for the Identification of Hazardous Waste
This document is organized in a manner similar to the way the definition and identification of
hazardous waste regulations are presented in Title 40 of the Code of Federal Regulations (CFR)
at Part 261.
Title 40: Protection of Environment
PART 261 – Identification and Listing of Hazardous Waste
Subpart C
§
261.3 Definition of hazardous waste
A solid waste, as defined in §
261.2, is a hazardous waste if:
(i) It exhibits any of the characteristics of hazardous waste identified in subpart C of this part.
However, any mixture of a waste from the extraction, beneficiation, and processing of ores and
minerals excluded under §261.4(b)(7) and any other solid waste exhibiting a characteristic of
hazardous waste under subpart C is a hazardous waste only if it exhibits a characteristic that
would not have been exhibited by the excluded waste alone if such mixture had not occurred, or
if it continues to exhibit any of the characteristics exhibited by the non-excluded wastes prior to
mixture. Further, for the purposes of applying the Toxicity Characteristic to such mixtures, the
mixture is also a hazardous waste if it exceeds the maximum concentration for any contaminant
listed in Table 1 to §261.24 that would not have been exceeded by the excluded waste alone if
the mixture had not occurred or if it continues to exceed the maximum concentration for any
contaminant exceeded by the nonexempt waste prior to mixture.
§ 261.3(a)(2)(i)
(a) A solid waste, as defined in §261.2, is a hazardous waste if:
(1) It is not excluded from regulation as a hazardous waste under §261.4(b); and
(2) It meets any of the following criteria:
(i) It exhibits any of the characteristics of hazardous waste identified in subpart C of this part.
However, any mixture of a waste from the extraction, beneficiation, and processing of ores and
minerals excluded under §
261.4(b)(7) and any other solid waste exhibiting a characteristic of
hazardous waste under subpart C is a hazardous waste only if it exhibits a characteristic that
would not have been exhibited by the excluded waste alone if such mixture had not occurred, or
if it continues to exhibit any of the characteristics exhibited by the non-excluded wastes prior to
mixture. Further, for the purposes of applying the Toxicity Characteristic to such mixtures, the
mixture is also a hazardous waste if it exceeds the maximum concentration for any contaminant
listed in table 1 to §
261.24 that would not have been exceeded by the excluded waste alone if the
9
mixture had not occurred or if it continues to exceed the maximum concentration for any
contaminant exceeded by the nonexempt waste prior to mixture.
§
261.3(b)(3)
(b) A solid waste which is not excluded from regulation under paragraph (a)(1) of this section
becomes a hazardous waste when any of the following events occur:
(1) In the case of a waste listed in subpart D of this part, when the waste first meets the listing
description set forth in subpart D of this part.
(2) In the case of a mixture of solid waste and one or more listed hazardous wastes, when a
hazardous waste listed in subpart D is first added to the solid waste.
(3) In the case of any other waste (including a waste mixture), when the waste exhibits any of the
characteristics identified in subpart C of this part.
§ 261.3(c)(1)
(c) Unless and until it meets the criteria of paragraph (d) of this section:
(1) A hazardous waste will remain a hazardous waste.
§ 261.3(d)(1)
(d) Any solid waste described in paragraph (c) of this section is not a hazardous waste if it meets
the following criteria:
(1) In the case of any solid waste, it does not exhibit any of the characteristics of hazardous
waste identified in subpart C of this part. (However, wastes that exhibit a characteristic at the
point of generation may still be subject to the requirements of part 268, even if they no longer
exhibit a characteristic at the point of land disposal.)
[57 FR 7632, Mar. 3, 1992; 57 FR 23063, June 1, 1992, as amended at 57 FR 37263, Aug. 18,
1992; 57 FR 41611, Sept. 10, 1992; 57 FR 49279, Oct. 30, 1992; 59 FR 38545, July 28, 1994; 60
FR 7848, Feb. 9, 1995; 63 FR 28637, May 26, 1998; 63 FR 42184, Aug. 6, 1998; 66 FR 27297,
May 16, 2001; 66 FR 50333, Oct. 3, 2001; 70 FR 34561, June 14, 2005; 70 FR 57784, Oct. 4,
2005; 71 FR 40258, July 14, 2006]
§
261.10 Criteria for identifying the characteristics of hazardous waste
(a) The Administrator shall identify and define a characteristic of hazardous waste in subpart C
only upon determining that:
(1) A solid waste that exhibits the characteristic may:
10
(i) Cause, or significantly contribute to, an increase in mortality or an increase in serious
irreversible, or incapacitating reversible, illness; or
(ii) Pose a substantial present or potential hazard to human health or the environment when it is
improperly treated, stored, transported, disposed of or otherwise managed; and
(2) The characteristic can be:
(i) Measured by an available standardized test method which is reasonably within the capability
of generators of solid waste or private sector laboratories that are available to serve generators of
solid waste; or
(ii) Reasonably detected by generators of solid waste through their knowledge of their waste.
(b) [Reserved]
PART 262 – Standards Applicable to Generators of Hazardous Waste
Subpart
§ 262.11 Hazardous waste determination
A person who generates a solid waste, as defined in 40 CFR 261.2, must determine if that waste
is a hazardous waste using the following method:
(a) He should first determine if the waste is excluded from regulation under 40 CFR 261.4.
(b) He must then determine if the waste is listed as a hazardous waste in subpart D of 40 CFR
part 261.
Note: Even if the waste is listed, the generator still has an opportunity under 40 CFR 260.22 to
demonstrate to the Administrator that the waste from his particular facility or operation is not a
hazardous waste.
(c) For purposes of compliance with
40 CFR part 268, or if the waste is not listed in subpart D of
40 CFR part 261, the generator must then determine whether the waste is identified in subpart C
of 40 CFR part 261 by either:
(1) Testing the waste according to the methods set forth in subpart C of 40 CFR part 261, or
according to an equivalent method approved by the Administrator under 40 CFR 260.21; or
(2) Applying knowledge of the hazard characteristic of the waste in light of the materials or the
processes used.
11
(d) If the waste is determined to be hazardous, the generator must refer to parts 261, 264, 265,
266, 268, and 273 of this chapter for possible exclusions or restrictions pertaining to
management of the specific waste.
[45 FR 33142, May 19, 1980, as amended at 45 FR 76624, Nov. 19, 1980; 51 FR 40637, Nov. 7,
1986; 55 FR 22684, June 1, 1990; 56 FR 3877, Jan. 31, 1991; 60 FR 25541, May 11, 1995]
General Resources for Hazardous Waste Characteristics
Representative Sampling
Appendix I to Part 261Representative Sampling Methods
The methods and equipment used for sampling waste materials will vary with the form and
consistency of the waste materials to be sampled. Samples collected using the sampling
protocols listed below, for sampling waste with properties similar to the indicated materials, will
be considered by the Agency to be representative of the waste.
[45 FR 33119, May 19, 1980, as amended at 70 FR 34562, June 14, 2005]
Sampling Plan
Test Methods for Evaluating Solid Waste, Physical/Chemical Methods (SW-846) - Sampling
Plan
Federal Register Notices
Final Rule and Interim Final Rule - Hazardous Waste Management System: General
45 FR 33066, May 19, 1980
Petroleum Refining Process Wastes - Notice of Data Availability
68 FR 59935, October 20, 2003
Letters/Memoranda
REGULATORY STATUS OF USED NICKEL CATALYST
STATUS OF SPENT SILVER-BEARING PHOTOFIXER THAT IS RECLAIMED
BIOSOLIDS
Ignitability
The regulations for the hazardous characteristic of ignitability can be found at 40 CFR 261.21.
12
Regulations for Ignitable Liquids
§ 261.21
(a) A solid waste exhibits the characteristic of ignitability if a representative sample of the waste
has any of the following properties:
(1) It is a liquid, other than an aqueous solution containing less than 24 percent alcohol by
volume and has flash point less than 60 °C (140 °F), as determined by a Pensky-Martens Closed
Cup Tester (incorporated by reference, see §260.11), or a Setaflash Closed Cup Tester, using the
test method specified in ASTM Standard D 3278–78 (incorporated by reference, see §
260.11).
Letters/Memoranda
DETERMINATION OF THE IGNITABILITY CHARACTERISTIC
USE OF PAINT FILTER LIQUIDS TEST TO DETERMINE FREE LIQUIDS IN A WASTE
MIXTURES OF USED OIL AND CHARACTERISTIC HAZARDOUS WASTE
USE OF ASTM METHOD D-56 IN IGNITABILITY DETERMINATIONS
POSITION PAPER ON SPENT ABSORBENT MATERIALS
DEFINING IGNITABLE LIQUIDS METHOD
RESPONSE TO SPECIFIC QUESTIONS REGARDING HAZARDOUS WASTE IDENTIFICATION
AND GENERATOR REGULATIONS
ALCOHOL-CONTENT EXCLUSION FOR THE IGNITABILITY CHARACTERISTIC
CLARIFICATION ON: MANIFEST DOCUMENT NUMBER; F003, F005, D001; WASTE DESTINED
FOR RECYCLING; AND TREATMENT STANDARDS FOR CFC
PRETREATMENT OF CHARACTERISTIC WASTES SUBJECT TO LAND DISPOSAL
RESTRICTIONS
AQUEOUS SOLUTION, IGNITABILITY DEFINED
AQUEOUS WASTE AS IGNITABLE
LIQUID WASTE, DEFINITION OF
CLARIFICATION OF THE RECYCLED USED OIL MANAGEMENT STANDARDS AS THEY
PERTAIN TO IGNITABLE USED OIL
CLARIFICATION OF THE USED OIL REGULATIONS APPLICABLE TO MIXTURES OF USED OIL
AND CHARACTERISTIC WASTE
DEFINITION OF A LIQUID AS IT APPLIES TO IGNITABLE AND CORROSIVE WASTES; LIQUID
AS IT APPLIES TO IGNITABLE OR CORROSIVE WASTES
13
IGNITABILITY OR CORROSIVITY TESTING-LIQUID AND AQUEOUS DEFINITION
FLASH POINT TESTS AND THE IGNITABILITY CHARACTERISTIC
DEFINITION OF AQUEOUS
Regulations for Ignitable Solids
§ 261.21(a)
(2) It is not a liquid and is capable, under standard temperature and pressure, of causing fire
through friction, absorption of moisture or spontaneous chemical changes and, when ignited,
burns so vigorously and persistently that it creates a hazard.
Letters/Memoranda
FLASH POINT TESTING OF A WASTE FIBROUS FILTER MATERIAL
INDUSTRIAL WIPERS AND THE HAZARDOUS WASTE IDENTIFICATION RULE
HOW IGNITABLE SOLIDS AND SOLVENT CONTAMINATED RAGS OR SHOP TOWELS FIT
INTO D001 CHARACTERISTIC OF IGNITABILITY
INTERPRETATION OF THE RCRA IGNITABILITY CHARACTERISTIC WITH REGARD TO
ACETONE WIPES
CHARACTERIZATION OF NITROCELLULOSE FILTER FABRIC WASTE
REGULATORY STATUS OF METAL CASINGS CONTAINING SPENT POWDERED METALLIC
OXIDE CATALYST
DETERMINATION OF THE IGNITABILITY CHARACTERISTIC
IGNITABLE SOLID DEFINITION APPLIED TO TITANIUM SWARF
IGNITABILITY CHARACTERISTIC TESTING FOR SOLIDS
CLARIFICATION OF THE CHARACTERISTIC OF IGNITABILITY AS IT PERTAINS TO SOLIDS
VS. LIQUIDS
IGNITABILITY CHARACTERISTIC, DEFINITION OF UNDER STANDARD TEMPERATURE AND
PRESSURE
Regulations for Ignitable Compressed Gas
§ 261.21(a)
(3) It is an ignitable compressed gas.
14
(i) The term “compressed gas” shall designate any material or mixture having in the container an
absolute pressure exceeding 40 p.s.i. at 70 °F or, regardless of the pressure at 70 °F, having an
absolute pressure exceeding 104 p.s.i. at 130 °F; or any liquid flammable material having a vapor
pressure exceeding 40 p.s.i. absolute at 100 °F as determined by ASTM Test D–323.
(ii) A compressed gas shall be characterized as ignitable if any one of the following occurs:
(A) Either a mixture of 13 percent or less (by volume) with air forms a flammable mixture or the
flammable range with air is wider than 12 percent regardless of the lower limit. These limits
shall be determined at atmospheric temperature and pressure. The method of sampling and test
procedure shall be acceptable to the Bureau of Explosives and approved by the director, Pipeline
and Hazardous Materials Technology, U.S. Department of Transportation (see Note 2).
(B) Using the Bureau of Explosives' Flame Projection Apparatus (see
Note 1), the flame projects
more than 18 inches beyond the ignition source with valve opened fully, or, the flame flashes
back and burns at the valve with any degree of valve opening.
(C) Using the Bureau of Explosives' Open Drum Apparatus (see
Note 1), there is any significant
propagation of flame away from the ignition source.
(D) Using the Bureau of Explosives' Closed Drum Apparatus (see Note 1), there is any explosion
of the vapor-air mixture in the drum.
Letters/Memoranda
INCINERATORS THAT RECEIVE GASEOUS EMISSIONS, RCRA EXCLUSION, CAA APPLIES
Regulations for Oxidizers
§ 261.21(a)
(4) It is an oxidizer. An oxidizer for the purpose of this subchapter is a substance such as a
chlorate, permanganate, inorganic peroxide, or a nitrate, that yields oxygen readily to stimulate
the combustion of organic matter (see Note 4).
(i) An organic compound containing the bivalent -O-O- structure and which may be considered a
derivative of hydrogen peroxide where one or more of the hydrogen atoms have been replaced
by organic radicals must be classed as an organic peroxide unless:
(A) The material meets the definition of a Class A explosive or a Class B explosive, as defined in
§261.23(a)(8), in which case it must be classed as an explosive,
(B) The material is forbidden to be offered for transportation according to
49 CFR 172.101
and 49 CFR 173.21,
15
(C) It is determined that the predominant hazard of the material containing an organic peroxide is
other than that of an organic peroxide, or
(D) According to data on file with the
Pipeline and Hazardous Materials Safety Administration
in the U.S. Department of Transportation (see
Note 3), it has been determined that the material
does not present a hazard in transportation.
Letters/Memoranda
APPLICABILITY OF HAZARDOUS WASTE CODES TO A CHEMICAL POLISHING SYSTEM
RCRA APPLICABILITY TO POTASSIUM PERMANGANATE AND MANGANESE DISPOSAL
NITRIC ACID WASTE CHARACTERIZATION
REGULATORY STATUS OF METAL CASINGS CONTAINING SPENT POWDERED METALLIC
OXIDE CATALYST
Regulations for the Hazardous Waste Number for Ignitability
§ 261.21
(b) A solid waste that exhibits the characteristic of ignitability has the EPA Hazardous Waste
Number of D001.
Note 1: A description of the Bureau of Explosives' Flame Projection Apparatus, Open Drum
Apparatus, Closed Drum Apparatus, and method of tests may be procured from the Bureau of
Explosives.
Note 2: As part of a U.S. Department of Transportation (DOT) reorganization, the Office of
Hazardous Materials Technology (OHMT), which was the office listed in the 1980 publication of
49 CFR 173.300 for the purposes of approving sampling and test procedures for a flammable
gas, ceased operations on February 20, 2005. OHMT programs have moved to the Pipeline and
Hazardous Materials Safety Administration (PHMSA) in the DOT.
Note 3: As part of a U.S. Department of Transportation (DOT) reorganization, the Research and
Special Programs Administration (RSPA), which was the office listed in the 1980 publication of
49 CFR 173.151a for the purposes of determining that a material does not present a hazard in
transport, ceased operations on February 20, 2005. RSPA programs have moved to the Pipeline
and Hazardous Materials Safety Administration (PHMSA) in the DOT.
Note 4: The DOT regulatory definition of an oxidizer was contained in §173.151 of 49 CFR, and
the definition of an organic peroxide was contained in paragraph 173.151a. An organic peroxide
is a type of oxidizer.
16
[45 FR 33119, May 19, 1980, as amended at 46 FR 35247, July 7, 1981; 55 FR 22684, June 1,
1990; 70 FR 34561, June 14, 2005; 71 FR 40259, July 14, 2006]
Letters/Memoranda
PRETREATMENT OF CHARACTERISTIC WASTES SUBJECT TO LAND DISPOSAL
RESTRICTIONS
REGULATORY REQUIREMENTS APPLICABLE TO TWO WASTE STREAMS THAT WOULD BE
BILAYERED THROUGH PHASE SEPARATION AT A LICENSED TSDF
SOLVENT-CONTAMINATED WASTEWATER FROM FRAGRANCE MANUFACTURE
END-USERS OF CHLORDIMEFORM EXEMPTION
MIXTURE OF METHANOL AND SOLID WASTE WHICH DOES NOT EXHIBIT ANY
CHARACTERISTICS
General Resources for the Ignitability Characteristic
Background document for the Ignitability characteristic
Test Methods
Test methods are not required by the Federal regulations to determine if a waste passes or
fails the characteristic of ignitability according to the RCRA regulatory definition at 40 CFR
261.21. To clarify, the test results of these methods cannot be used to directly classify a waste as
a D001 hazardous waste, nor can the results be used by themselves to definitively classify a
waste as non-hazardous. No specific test for defining ignitable solids or oxidizers is required by
the RCRA regulations, and only a waste meeting the narrative regulatory definitions at 40 CFR
261.21(a)(2) and/or 261.21(a)(4) is an ignitable hazardous waste because it is an ignitable solid
and/or an oxidizer. However, these test methods were developed to specifically illustrate the
ignitable and oxidizer properties of materials, including wastes, and their results provide relevant
and useful information that may be applied to knowledge of a waste in determining whether a
waste meets the 40 CFR 261.21(a) criteria.
SW-846 Test Method for Ignitability of Solids – Test Method 1030
SW-846 Test Method for Oxidizing Solids – Test Method 1040
SW-846 Test Method to Determine Substances Likely to Spontaneously Combust -
Test
Method 1050
Test Methods for Evaluating Solid Waste, Physical/Chemical Methods (SW-846) –
Sampling Plan
17
Federal Register Notices
Proposed Rule – Hazardous Waste Guidelines and Regulations: 43 FR 58946, December
18, 1978
Final Rule - Land Disposal Restrictions for Third Third Scheduled Wastes
55 FR 22520, June 1, 1990
Proposed Rule – Hazardous Waste Management System; Testing and Monitoring
Activities: 58 FR 46052, August 31, 1993
Proposed Rule – Land Disposal Restrictions Phase IV: Treatment Standards for Wood
Preserving Wastes, Exemptions from RCRA for Certain Processed Materials/Mineral
Processing and Bevill Exclusion Issues and the Use of Hazardous Waste as Fill: 62 FR
25997, May 12, 1997
Proposed Rule – Hazardous Waste Management System; Testing and Monitoring
Activities: 58 FR 46052, August 31, 1993
Corrosivity
The regulations for the hazardous characteristic of corrosivity can be found at 40 CFR 261.22.
Regulations for Aqueous Solutions
§ 261.21
(a) A solid waste exhibits the characteristic of corrosivity if a representative sample of the waste
has either of the following properties:
(1) It is aqueous
and has a pH less than or equal to 2 or greater than or equal to 12.5, as
determined by a pH meter using
Method 9040C in “Test Methods for Evaluating Solid
Waste, Physical/Chemical Methods,” EPA Publication SW–846, as incorporated by
reference in §260.11 of this chapter.
Federal Register Notice
Final Rule: Hazardous Waste Management System: Testing and Monitoring Activities
(Evaluating Aqueousness) 60 FR 3089, January 13, 1995
Letters/Memoranda
INTERPRETATION OF "AQUEOUS" AS APPLIED TO THE CORROSIVITY CHARACTERISTIC
“AQUEOUS” AS APPLIED TO THE CORROSIVITY CHARACTERISTIC
18
USE OF PAINT FILTER LIQUIDS TEST TO DETERMINE FREE LIQUIDS IN A WASTE
CORROSIVE CHARACTERISTIC APPLIED TO LIQUID AND AQUEOUS WASTES
IGNITABILITY OR CORROSIVITY TESTING-LIQUID AND AQUEOUS DEFINITION
APPLICABILITY OF CORROSIVITY PH AND STEEL CORROSION TESTS
DEFINITION OF A LIQUID AS IT APPLIES TO IGNITABLE AND CORROSIVE WASTES; LIQUID
AS IT APPLIES TO IGNITABLE OR CORROSIVE WASTES
PH MEASUREMENT ON PARTIAL SOLIDS
Regulations for Steel Corrosivity
§ 261.22(a)
(2) It is a liquid and corrodes steel (SAE 1020) at a rate greater than 6.35 mm (0.250 inch) per
year at a test temperature of 55 °C (130 °F) as determined by Method 1010A in “Test Methods
for Evaluating Solid Waste, Physical/Chemical Methods,” EPA Publication SW–846, and as
incorporated by reference in §260.11 of this chapter.
Letters/Memoranda
SW-846 TEST METHODS
AGITATE SAMPLES EVALUATED USING METHOD 1110
SPENT PICKLE LIQUOR CORROSIVITY
Regulations for the Hazardous Waste Number for Corrosivity
§ 261.22
(b) A solid waste that exhibits the characteristic of corrosivity has the EPA Hazardous Waste
Number of D002.
[45 FR 33119, May 19, 1980, as amended at 46 FR 35247, July 7, 1981; 55 FR 22684, June 1,
1990; 58 FR 46049, Aug. 31, 1993; 70 FR 34561, June 14, 2005]
Letters/Memoranda
CORROSIVITY CHARACTERISTIC AS IT APPLIES TO SOLIDS
LAND DISPOSAL RESTRICTION INTERIM FINAL RULE
PRECIPITATION WHICH IS CORROSIVE DUE TO CONTACT WITH EXEMPT WASTES (COAL
GASIFICATION ASH)
19
NITRIC ACID WASTE CHARACTERIZATION
ELEMENTARY NEUTRALIZATION UNITS GENERATING AND STORING NON-CORROSIVE
HAZARDOUS WASTES
POLLUTION CONTROL SLUDGE FROM TREATMENT OF MINING WASTE - EXCLUSION
CEMENT KILN DUST WASTE
BATTERIES, WASTE ELECTROLYTE FROM RECHARGEABLE NICKEL-CADMIUM
BATTERIES, SCRAP METAL, AND PRECIOUS METALS
FOOD PROCESSORS, IMPACT OF HAZARDOUS WASTE REGULATIONS ON
LIQUID, FREE LIQUID, RELEASABLE LIQUID DEFINITIONS
REGULATORY STATUS OF LABORATORY WASTEWATER
General Resources for the Corrosivity Characteristic
Background document for the Corrosivity Characteristic
"Determination of Water in Waste Materials by Karl Fisher Titration." – Method 9000
Test Methods for Evaluating Solid Waste, Physical/Chemical Methods (SW-846) -
Sampling Plan
Determination of Water in Waste Materials by Quantitative Calcium Hydride Reaction;
Method 9001
Corrosivity Definition of Aqueous
Reactivity
The regulations for the hazardous characteristic of reactivity can be found at 40 CFR 261.23.
Regulations for Reactivity
§
261.23
(a) A solid waste exhibits the characteristic of reactivity if a representative sample of the waste
has any of the following properties:
20
(1) It is normally unstable and readily undergoes violent change without detonating.
Regulations for Reactivity with Water
§ 261.23(a)
(2) It reacts violently with water.
(3) It forms potentially explosive mixtures with water.
(4) When mixed with water, it generates toxic gases, vapors or fumes in a quantity sufficient to
present a danger to human health or the environment.
Letters/Memoranda
CHEMICAL AGENTS GB, VX, AND HD AT MUNITIONS DISPOSAL FACILITY
REGULATION AND DISPOSAL REQUIREMENTS FOR SODIUM AZIDE
Regulations for Cyanide/Sulfide Reactivity
§ 261.23(a)
(5) It is a cyanide or sulfide bearing waste which, when exposed to pH conditions between 2 and
12.5, can generate toxic gases, vapors or fumes in a quantity sufficient to present a danger to
human health or the environment.
Letters/Memoranda
WITHDRAWAL OF CYANIDE AND SULFIDE GUIDANCE
HAZARDOUS WASTE TESTING ISSUES
Regulations for Explosives
§
261.23(a)
(6) It is capable of detonation or explosive reaction if it is subjected to a strong initiating source
or if heated under confinement.
(7) It is readily capable of detonation or explosive decomposition or reaction at standard
temperature and pressure.
21
(8) It is a forbidden explosive as defined in 49 CFR 173.51, or a Class A explosive as defined in
49 CFR 173.53 or a Class B explosive as defined in 49 CFR 173.88.
Letters/Memoranda
TRANSPORTATION AND DISPOSAL OF SHOCK SENSITIVE OR EXPLOSIVE MATERIALS
DOT REGULATIONS REFERENCED IN THE RCRA REGULATIONS
REGULATORY ISSUES PERTAINING TO WASTES CONTAMINATED WITH EXPLOSIVE
RESIDUES
REACTIVE WASTE - EXPLOSIVITY
Regulations for the Hazardous Waste Number for Reactivity
§ 261.23
(b) A solid waste that exhibits the characteristic of reactivity has the EPA Hazardous Waste
Number of D003.
[45 FR 33119, May 19, 1980, as amended at 55 FR 22684, June 1, 1990]
Letters/Memoranda
Aerosols
BUBBLER CANISTERS CONTAINING PHOSPHOROUS OXYCHLORIDE ARE NOT WASTE
WHEN RETURNED TO THE UNITED STATES FROM JAPAN FOR REGENERATION
REGULATORY STATUS OF WASTE AEROSOL CANS
CLARIFICATION OF REACTIVITY CHARACTERISTIC AS IT PERTAINS TO AEROSOL CANS
REGULATORY STATUS OF USED RESIDENTIAL AND COMMERCIAL/INDUSTRIAL AEROSOL
CANS
Ammunition
REGULATORY STATUS OF METAL CASINGS CONTAINING SPENT POWDERED METALLIC
OXIDE CATALYST
SMALL ARMS AMMUNITION REACTIVITY, OFF SPECIFICATION
CLARIFICATION OF DISCARDED AMMUNITION OF 0.50 CALIBER
Batteries
22
REACTIVE CHARACTERISTICS OF DISCHARGED LI/SO2 BATTERIES
REGULATORY STATUS OF SPENT/DISCARDED LITHIUM-SULFUR DIOXIDE BATTERIES
WASTE CHARACTERIZATION: LITHIUM BATTERIES
REGULATORY STATUS OF BATTERIES
Flameless Ration Heaters
CLASSIFICATION AND DISPOSAL OF UNUSED FLAMELESS RATION HEATERS
APPLICABILITY OF RCRA TO DISPOSAL OF UNIFIED GROUP RATION - EXPRESS (UGR-E)
STATUS OF WASTE HYDROGEN FREE RATION HEATERS (HRHs)
Explosives
BLASTING CAPS AS REACTIVE WASTES
DETONATING EXPLOSIVE WASTES
DISCARDED CLASS C EXPLOSIVES
General
LEAKS, SPILLS, AND ILLEGAL DISCHARGES OF LISTED WASTES TO SURFACE WATERS,
MIXTURE RULE APPLIED TO
REGULATORY STATUS OF UNIT AND WASTE IF NONHAZARDOUS WASTE BECOMES
REACTIVE WHEN DEWATERED
RCRA HAZARDOUS WASTE DETERMINATION OF SPENT NUCLEAR REACTOR FUELS
APPLICABILITY OF 40 CFR 261.5 TO K047
DREDGE SEDIMENTS (See Note 5)
Note 5:
§261.4(g) Exclusions
(g) Dredged material that is not a hazardous waste. Dredged material that is subject to the
requirements of a permit that has been issued under 404 of the Federal Water Pollution Control
Act (33 U.S.C.1344) or section 103 of the Marine Protection, Research, and Sanctuaries Act of
1972 (33 U.S.C. 1413) is not a hazardous waste. For this paragraph (g), the following definitions
apply:
(1) The term dredged material has the same meaning as defined in 40 CFR 232.2;
[45 FR 33119, May 19, 1980]
23
Federal Register Notice
Military Munitions Rule
62 FR 6622, February 12, 1997
General Resources for the Reactivity Characteristic
Background document for the Reactivity characteristic
Toxicity
The regulations for the hazardous characteristic of toxicity can be found at 40 CFR 261.24.
Regulations for Toxicity
§261.24
(a) A solid waste (except manufactured gas plant waste) exhibits the characteristic of toxicity if,
using the Toxicity Characteristic Leaching Procedure, test Method 1311 in “Test Methods for
Evaluating Solid Waste, Physical/Chemical Methods,” EPA Publication SW–846, as
incorporated by reference in §260.11 of this chapter, the extract from a representative sample of
the waste contains any of the contaminants listed in table 1 at the concentration equal to or
greater than the respective value given in that table. Where the waste contains less than 0.5
percent filterable solids, the waste itself, after filtering using the methodology outlined in
Method 1311, is considered to be the extract for the purpose of this section.
(b) A solid waste that exhibits the characteristic of toxicity has the EPA Hazardous Waste
Number specified in Table 1 which corresponds to the toxic contaminant causing it to be
hazardous.
Table 1 —Maximum Concentration of Contaminants for the Toxicity Characteristic
EPA HW No.
1
Contaminant CAS No.
2
Regulatory Level (mg/L)
D004 Arsenic 7440–38–2 5.0
D005 Barium 7440–39–3 100.0
D018 Benzene 71–43–2 0.5
D006 Cadmium 7440–43–9 1.0
D019 Carbon tetrachloride 56–23–5 0.5
D020 Chlordane 57–74–9 0.03
D021 Chlorobenzene 108–90–7 100.0
D022 Chloroform 67–66–3 6.0
24
D007 Chromium 7440–47–3 5.0
D023 o-Cresol 95–48–7
4
200.0
D024 m-Cresol 108–39–4
4
200.0
D025 p-Cresol 106–44–5
4
200.0
D026 Cresol
4
200.0
D016 2,4-D 94–75–7 10.0
D027 1,4-Dichlorobenzene 106–46–7 7.5
D028 1,2-Dichloroethane 107–06–2 0.5
D029 1,1-Dichloroethylene 75–35–4 0.7
D030 2,4-Dinitrotoluene 121–14–2
3
0.13
D012 Endrin 72–20–8 0.02
D031 Heptachlor (and its epoxide) 76–44–8 0.008
D032 Hexachlorobenzene 118–74–1
3
0.13
D033 Hexachlorobutadiene 87–68–3 0.5
D034 Hexachloroethane 67–72–1 3.0
D008 Lead 7439–92–1 5.0
D013 Lindane 58–89–9 0.4
D009 Mercury 7439–97–6 0.2
D014 Methoxychlor 72–43–5 10.0
D035 Methyl ethyl ketone 78–93–3 200.0
D036 Nitrobenzene 98–95–3 2.0
D037 Pentrachlorophenol 87–86–5 100.0
D038 Pyridine 110–86–1
3
5.0
D010 Selenium 7782–49–2 1.0
D011 Silver 7440–22–4 5.0
D039 Tetrachloroethylene 127–18–4 0.7
D015 Toxaphene 8001–35–2 0.5
D040 Trichloroethylene 79–01–6 0.5
D041 2,4,5-Trichlorophenol 95–95–4 400.0
D042 2,4,6-Trichlorophenol 88–06–2 2.0
25
D017 2,4,5-TP (Silvex) 93–72–1 1.0
D043 Vinyl chloride 75–01–4 0.2
1
Hazardous waste number.
2
Chemical abstracts service number.
3
Quantitation limit is greater than the calculated regulatory level. The quantitation limit therefore
becomes the regulatory level.
4
If o-, m-, and p-Cresol concentrations cannot be differentiated, the total cresol (D026)
concentration is used. The regulatory level of total cresol is 200 mg/l.
[55 FR 11862, Mar. 29, 1990, as amended at 55 FR 22684, June 1, 1990; 55 FR 26987, June 29,
1990; 58 FR 46049, Aug. 31, 1993; 67 FR 11254, Mar. 13, 2002; 71 FR 40259, July 14, 2006]
General Resources for the Toxicity Characteristic
Methods for Determining Characteristics of Hazardous Waste, SW-846, Chapter 8
Federal Register Notices
Final Rule: Toxicity Characteristic
55 FR 11829: March 29, 1,90
Proposed Rule: Hazardous Waste Management System; Modification of the Hazardous
Waste Recycling Regulatory Program
58 FR 8102, February 11, 1993
Request for Comment on Proposed Statement of Policy Regarding Spent Antifreeze
63 FR 20187, April 23, 1998
Letters/Memoranda
Antifreeze
USED AUTOMOBILE ANTIFREEZE DISPOSAL
SPENT ANTI-FREEZE COOLANT REGULATORY STATUS
SPENT ANTIFREEZE AND THE TOXICITY CHARACTERISTIC
Biosolids
BIOSOLIDS
Chromium/Trivalent Chromium
HAZARDOUS WASTE TESTING ISSUES
26
RULEMAKING PETITION FOR TRIVALENT CHROMIUM EXCLUSION
PETITION PROCESS FOR THE TRIVALENT CHROMIUM EXCLUSION
TOTAL CHROMIUM ANALYSIS
Chromated Copper Arsenate (CCA) Treated Wood
CCA TREATED WOOD WHEN DISPOSED
WOOD MULCH DERIVED FROM WASTE LUMBER PRESERVED WITH CHROMATED COPPER
ARSENATE (CCA)
RECOMMENDATION ON THE DISPOSAL OF WASTE LUMBER PRESERVED WITH
CHROMATED COPPER ARSENATE (CCA)
CURRENT STATUS OF CCA-TREATED WOOD UNDER RCRA
Explosive Waste/Military Munitions
APPLICABILITY OF THE TCLP TO WASTE MUNITIONS
TCLP PARTICLE SIZE REDUCTION EXEMPTION FOR MUNITIONS
COMBUSTION PROHIBITION AND EXPLOSIVE WASTES
Lead/Lead-Based Paint
LEADED PAINT SANDBLASTING WASTE TESTING USING TCLP
TCLP AND LEAD PAINT REMOVAL DEBRIS
LEAD PAINT REMOVAL DEBRIS AND THE TCLP PROCEDURE
RCRA APPLICABILITY TO PAINT REMOVAL WASTES
INCORPORATION OF PRETOX 2000 INTO LEADED PAINT STRIPPER
RECYCLING OF MOLDING AND CASTING SANDS
LEACH TESTING PROCEDURE TO REMOVE LEAD-CONTAMINATED SOILS FROM
RESIDENTIAL AREAS
MANAGEMENT AND DISPOSAL OF WASTE VINYL MINI BLINDS
PROPOSED TSCA 403 SOIL LEAD HAZARD AND OSWER'S LEAD-IN-SOILS POLICY
Manufactured Gas Plant (MGP)
IMPLEMENTATION OF VACATURE OF TCLP USE FOR EVALUATING MANUFACTURED GAS
PLANT (MGP) WASTES IN THE BATTERY RECYCLERS CASE
MANUFACTURED GAS PLANT (MGP) REMEDIATION WASTE
27
Mercury/Mercury Lamps
MANAGEMENT OF USED FLUORESCENT LAMPS
STATUS OF FLUORESCENT LAMPS UNDER RCRA
DETERMINATION ON WHETHER A GENERATOR'S FLUORESCENT TUBES ARE
NONHAZARDOUS
MANAGEMENT OF USED FLUORESCENT LAMPS
MERCURY DRY CELL BATTERIES AND APPLICABLE REGULATIONS
WASTE IDENTIFICATION OF DISCARDED THERMOMETERS
Municipal Waste Combustion Ash
SAMPLING AND ANALYSIS OF MUNICIPAL REFUSE INCINERATOR ASH; Draft 05/15/1994
GUIDANCE FOR THE SAMPLING AND ANALYSIS OF MUNICIPAL WASTE COMBUSTION ASH
FOR THE TOXICITY CHARACTERISTIC; June 1995
STATUS OF MUNICIPAL WASTE COMBUSTION ASH
RESIDUES FROM MUNICIPAL WASTE RESOURCE RECOVERY FACILITIES; MUNICIPAL
WASTE COMBUSTION RESIDUES-ASH AND SLUDGE
MUNICIPAL WASTE COMBUSTION, DISPOSAL OF RESIDUAL ASH
Oily Waste/Used Oil
USED OIL FILTERS CLASSIFICATION
TC RULE RELATIONSHIP TO USED OIL FILTER DISPOSAL
APPLICABILITY OF THE TOXICITY CHARACTERISTIC TO USED OIL FILTERS
TC RULE DELAY OF IMPOSITION ON OIL FILTERS
TCLP EXTRACTIONS APPLIED TO LIQUID WASTES, OILS AND SOLVENT-BASED PRODUCTS
TCLP EXTRACTIONS AS THEY APPLY TO OILY WASTE
QUESTIONS ON FINAL USED OIL RULE
DILUTION OF TEST SAMPLING
USED OIL USED FOR DUST SUPPRESSION OR ROAD TREATMENT
CLARIFICATION OF THE USED OIL REGULATIONS APPLICABLE TO MIXTURES OF USED OIL
AND CHARACTERISTIC WASTE
28
REGULATORY REQUIREMENTS PERTAINING TO THE MANAGEMENT OF WASTE SOLVENTS
AND USED OIL
Toxicity Characteristic Leaching Procedure (TCLP)
SAMPLE HOLDING TIMES AND VALIDITY OF ANALYTICAL RESULTS
DILUTION OF TEST SAMPLING
EXEMPTION FROM PARTICLE SIZE REDUCTION STEP IN TCLP
MATRIX SPIKE IN TCLP PROCEDURE
ANALYSIS OF FLUFF MATERIALS
GENERATOR HAZARDOUS WASTE DETERMINATION AND THE TCLP
APPLICABILITY OF THE TCLP
APPLICABILITY OF THE TOXICITY CHARACTERISTIC AND THE TCLP
BIAS CORRECTION APPLIED TO THE TCLP
TC RULE HAZARDOUS WASTE DETERMINATION
SEMI-VOLATILE CONSTITUENT ANALYSIS AND ANALYTICAL LEVEL OF DETECTION
LIMITATIONS OF THE TOXICITY CHARACTERISTIC LEACHING PROCEDURE (TCLP)
INTERPRETATION OF THE PHRASE ""WHICH CAN BE REASONABLY EXPECTED TO BE
PRESENT"" FOR SOIL THAT EXHIBITS THE TOXICITY CHARACTERISTIC
INAPPROPRIATE USE OF METHOD 1311 (TCLP) AS AN ALTERNATIVE EXTRACTION
PROCEDURE
REVISIONS TO THE TCLP
SEMI-VOLATILE CONSTITUENT ANALYSIS AND ANALYTICAL LEVEL OF DETECTION
LIMITATIONS OF THE TOXICITY CHARACTERISTIC LEACHING PROCEDURE (TCLP)
ENVIRONMENTAL FACT SHEET: EPA REVISES QUALITY ASSURANCE MEASURES FOR THE
TOXICITY CHARACTERISTIC LEACHING PROCEDURE
Use of Totals to Determine Whether a Solid Waste Exhibits the Toxicity Characteristic
USE OF TOTAL WASTE ANALYSIS IN TOXICITY CHARACTERISTIC DETERMINATIONS
CALCULATION OF TCLP CONCENTRATIONS FROM TOTAL CONCENTRATIONS
BIOSOLIDS
TOTAL CONCENTRATION USED TO DEMONSTRATE A WASTE DOES NOT EXHIBIT THE
CHARACTERISTIC OF EP TOXICITY
GENERATOR USE OF TOTAL CONSTITUENT ANALYSIS IN LIEU OF THE EP OR TCLP TESTS
29
TOTAL CONSTITUENT ANALYSIS TO DETERMINE HAZARDOUS CHARACTERISTICS OF
WASTE SAMPLE
TOTAL WASTE ANALYSIS ON POTW BIOSOLIDS AND CERCLA LIABILITY
General Toxicity
RCRA HAZARDOUS WASTE DETERMINATION OF SPENT NUCLEAR REACTOR FUELS
RESPONSE TO REQUEST FOR OPINION ON SECTION 21 PETITION ON BATTERY DEPOSITS
NOTES ON RCRA METHODS AND QA ACTIVITIES
QC REVIEW OF PERMIT DATA
CLARIFICATION OF NEWLY LISTED WASTES AND HAZARDOUS DEBRIS
DESIGNATION OF AMERICIUM BERYLLIUM SOURCES UNDER RCRA
BATTERIES, WASTE ELECTROLYTE FROM RECHARGEABLE NICKEL-CADMIUM
REGULATORY STATUS OF PETROLEUM CONTAMINATED MEDIA AND DEBRIS UNDER THE
TOXICITY CHARACTERISTIC UST TEMPORARY DEFERRAL
REGULATORY STATUS OF BRASS PARTICLES GENERATED IN THE BELTING AND BUFFING
OF BRASS CASTINGS
REMOVAL OF TOXICITY CHARACTERISTIC WASTES FROM A SURFACE IMPOUNDMENT
PETROLEUM-CONTAMINATED MEDIA AND DEBRIS DEFERRAL FROM THE TOXICITY
CHARACTERISTIC
LAND DISPOSAL RESTRICTIONS (LDR) TREATMENT STANDARDS AND DISPOSAL OPTIONS
FOR CONTAMINATED SOIL
ELECTRIC UTILITY POLES
TC APPLICABILITY TO MIXED WASTE
TC RULE HAZARDOUS WASTE DETERMINATION
SQG COMPLIANCE WITH TC RULE
EPA'S NON-OBJECTION TO IMPORTS OF COBALT OXIDE-MOLYBDIC OXIDE SPENT
CATALYSTS INTO THE U.S. FOR RECOVERY
SLUDGES WITHIN SURFACE IMPOUNDMENTS, NEWLY REGULATED DUE TO TC RULE
SILVER IN WASTES AND IN SEWER DISCHARGES FROM THE PHOTO-FINISHING INDUSTRY
30