United Solid Waste EPA530-R-99-052
Environmenta Emergency PB2000-101 892
Protection (5305W February 2000
RCRA, Superfund & EPCRA
Hotline Training Module
Introduction to:
Hazardous Waste Incinerators
(40 CFR Parts 264/265, Subpart O)
Updated August 1999
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DISCLAIMER
This document was developed by Booz-Allen& Hamilton Inc. under contract 68-W 0-0039 to EPA. It is intended to
be used as a training tool for Hotline specialists and does not represent a statement ofEPA policy.
The information in this document is not by any means a complete representation ofEPA's regulations or policies.
This document is used only in the capacity of the Hotline training and is not use das a reference too Ion Hotline calls.
The Hotline revises and updates this document as regulatory pro gram areas change.
The information in this docume ntmay not necessarily reflect the current position of the Agency. This document is
not intended and cannot be relied upon to create any rights, substantive or procedural, enforceable by any party in
litigation with the United States.
RCRA, Superfund & EPCRA Hotline Phone Numbers
National toll-free (outside of DC area) (800) 424-9346
Local number (within DC area) (703) 412-9810
National toll-free for the hearing impaired (TDD) (800) 553-7672
Tne Hotline is open from 9 am to 6 pm Eastern Time,
Monday through Friday, except for federal holidays.
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HAZARDOUS WASTE INCINERATORS
CONTENTS
1. Introduction 1
2. Regulatory Summary 2
2.1 Overview of Combustion 2
2.2 Subpart O Applicability 3
2.3 Performance Standards 4
2.4 Operating Conditions 5
2.5 Permit Phases 6
2.6 Waste Analysis 7
2.7 Monitoring and Inspections 8
2.8 Management of Residues 8
2.9 Closure 8
2.10 Comparison of Permitted and Interim Status Incinerators 9
3. Regulatory Developments 11
4. Special Issues 13
4.1 Omnibus Permitting Authority 13
4.2 Public Participation 13
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Hazardous Waste Incinerators - 1
1. INTRODUCTION
Incineration is a commonly employed technology used to destroy hazardous waste.
When Congress enacted the Resource Conservation and Recovery Act (RCRA) in 1976,
it directed EPA to establish performance, design, and operating standards for all
hazardous waste treatment, storage, and disposal facilities (TSDFs). EPA promulgated
both general facility standards that apply to all TSDFs and requirements for specific
types of units (e.g., incinerators, landfills, and surface impoundments) in 40 CFR Parts
264 and 265. The regulations under Parts 264 and 265, Subpart O, apply to owners and
operators of facilities that incinerate hazardous waste.
This training module introduces the concept of burning hazardous wastes in units
regulated under RCRA and outlines the requirements for one type of device — the
incinerator. When you have completed this module you will be able to explain what an
incinerator is, understand how incinerators are regulated, and apply the appropriate
regulations when assisting Hotline callers. Specifically, you will be able to:
• State the conditions under which an owner/operator may be exempt from
Subpart O
• Define principal organic hazardous constituent (POHC) and describe the criteria
under which a POHC is selected
• Define destruction and removal efficiency (DRE)
• Describe the interaction between compliance with performance standards and
compliance with incinerator operating conditions established in a permit
• Understand the definition and purpose of a "trial burn."
Use this list of objectives to check your knowledge of this topic after you complete the
training session.
The information in this document is not by any means a complete representation of EPA's regulations or policies,
but is an introduction to the topic used for Hotline training purposes.
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2 - Hazardous Waste Incinerators
2. REGULATORY SUMMARY
Waste materials are burned in incinerators, boilers, and industrial furnaces for various
purposes. The purpose of the burning is directly related to the type of device.
Incinerators are used primarily for the destruction of hazardous constituents; however,
some energy or material recovery may occur. Boilers and industrial furnaces, on the
other hand, may burn wastes not only for destruction, but also to achieve significant
energy or materials recovery. The regulations that apply to each activity vary with the
type of waste that is burned, the type of combustion device, and the purpose of the
burning.
The Subpart O standards for hazardous waste incinerators primarily regulate the
emissions that result from the combustion process. Specifically, the regulations restrict
the emissions of organics, hydrogen chloride (HC1), and particulate matter (PM), as well
as fugitive emissions. A very important aspect of the regulations is that compliance
with operating conditions specified in the permit is deemed to be compliance with the
limits for organics, HC1, and PM.
Incinerators in existence on May 19,1980, were allowed to continue burning hazardous
waste if the units complied with the Part 265, Subpart O, interim status standards. On
November 8,1989, however, interim status terminated for all existing hazardous waste
incinerators unless the owner/operator had submitted a Part B permit application by
November 8,1986 (§270.73(f)). Due to this deadline, there are very few incinerators
presently operating under interim status. This module, therefore, focuses primarily on
the requirements for permitted, rather than interim status, incinerators. There is a
comparison of the requirements for permitted and interim status incinerators at the end
of this module.
2.1 OVERVIEW OF COMBUSTION
To facilitate an understanding of the Subpart O regulations, it is important to be
familiar with the combustion process itself. Incineration is the controlled burning of
substances in an enclosed area. During a burn, wastes are fed into the incinerator's
combustion chamber. As the wastes are heated, they are converted from solids and
liquids into gases. These gases pass through the flame and are heated further.
Eventually, the gases become so hot that the organic compounds in the gases break
down into their constituent atoms. These atoms combine with oxygen and form stable
gases that are released to the atmosphere after passing through air pollution control
devices (APCDs).
For incineration to be an effective method for destroying wastes' hazardous properties,
combustion must be complete. Three critical factors ensure the completeness of
The information in this document is not by any means a complete representation of EPA's regulations or policies,
but is an introduction to the topic used for Hotline training purposes.
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Hazardous Waste Incinerators - 3
combustion in an incinerator: (1) the temperature in the combustion chamber, (2) the
length of time wastes are maintained at high temperatures, and (3) the turbulence, or
degree of mixing, of the wastes and the air. Operating conditions are specified in each
incinerator permit to ensure that these factors are present to promote complete
combustion.
The stable gases produced by incineration are primarily carbon dioxide and water.
Depending on waste composition, however, small quantities of carbon monoxide,
nitrogen oxides, HC1, and other gases may form. Also, if combustion is not complete
compounds known as product of incomplete combustion (PICs) may be emitted. RCRA
regulations control the amount of HC1 released from the APCD.
Another by-product of the combustion process is ash. Ash is an inert solid material
composed primarily of carbon, salts, and metals. During combustion, most ash collects
at the bottom of the combustion chamber (bottom ash). When this ash is removed from
the combustion chamber, it may be considered hazardous waste via the derived-f rom
rule or because it exhibits a characteristic. Some ash, however, is carried up with the
gases as small particles, or particulate matter. These particles are also collected in the
APCD in accordance with RCRA-established limits.
As a hazardous waste management practice, incineration has several unique attributes.
First, if properly conducted, it permanently destroys toxic organic compounds
contained in hazardous waste by breaking their chemical bonds and reverting them to
their constituent elements, thereby reducing or removing their toxicity. Second,
incineration reduces the volume of hazardous waste by converting solids and liquids to
ash. Land disposal of ash, as opposed to untreated hazardous waste, is therefore both
safer and more efficient. Incineration, however, will not destroy inorganic compounds,
such as metals, present in hazardous waste. Residue ash from incinerators is subject to
applicable RCRA standards and may need to be treated for metals or other nonorganic
constituents prior to land disposal.
2.2 SUBPART O APPLICABILITY
The Subpart O standards apply to units that treat or destroy hazardous waste and
which meet the definition of an incinerator. An incinerator is any enclosed device that
uses controlled flame combustion and does not meet the criteria for classification as a
boiler, sludge dryer, carbon regeneration unit, or industrial furnace (§260.10). Typical
incinerators include rotary kilns, liquid injectors, controlled air incinerators, and
fluidized bed incinerators. The definition of incinerator also includes units that meet
the definition of infrared incinerator or plasma arc incinerator. An infrared incinerator
is any enclosed device that uses electric-powered resistance as a source of heat and
which is not listed as an industrial furnace. A plasma arc incinerator is any enclosed
device using a high intensity electrical discharge as a source of heat which is not listed
as an industrial furnace.
The information in this document is not by any means a complete representation of EPA's regulations or policies,
but is an introduction to the topic used for Hotline training purposes.
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4 - Hazardous Waste Incinerators
All devices classified as incinerators which burn hazardous waste must follow the
Subpart O standards, with the following exception. The Regional Administrator must
exempt an owner/opera tor applying for a permit from all of the incinerator standards
in Subpart O, except waste analysis and closure, if the hazardous waste fed into an
incinerator is considered low risk waste (§264.340(b)). The criteria for defining a waste
as low risk are:
• The waste is a hazardous waste listed in Part 261, Subpart D, or identified in
Subpart C only for ignitability, corrosivity, or both
or
• The waste is a hazardous waste listed in Part 261, Subpart D, or identified in
Subpart C only for reactivity, and will not be burned with other hazardous
wastes (this exemption does not apply to wastes that are reactive for generating
toxic gases when mixed with water (§261.23(a)(4), or cyanide or sulfide gases
(§261.23(a)(5))
and
• The waste contains none of the hazardous constituents listed in Appendix VTfl of
Part 261.
2.3 PERFORMANCE STANDARDS
The Subpart O standards for hazardous waste incinerators set performance standards
which limit the quantity of gaseous emissions an incinerator may release. Specifically,
the regulations set limits on the emission of organics, HC1, and PM. The following
section outlines the requirements for each of these substances.
ORGANICS
To obtain a permit, an owner/operator must demonstrate that emission levels set for
various hazardous organic constituents are not exceeded. EPA's principle measure of
incinerator performance is its destruction and removal efficiency (DRE). A 99.99
percent DRE means that one molecule of an organic compound is released to the air for
every 10,000 molecules entering the incinerator. A 99.9999 percent DRE means that one
molecule of an organic compound is released to the air for every one million molecules
entering the incinerator.
Since it would be impossible to monitor the DRE results for every organic constituent
contained in a waste, certain principal organic hazardous constituents (POHCs) are
selected for monitoring and are designated in the permit. POHCs are selected based on
high concentration in the waste feed and difficulty in burning compared to other
The information in this document is not by any means a complete representation of EPA's regulations or policies,
but is an introduction to the topic used for Hotline training purposes.
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Hazardous Waste Incinerators - 5
organic compounds. If the incinerator achieves the required DRE for the selected
POHCs, then it is presumed that the incinerator should achieve the same or better DRE
for organic compounds that are easier to incinerate.
RCRA performance standards require a minimum DRE of 99.99 percent for POHCs
designated in the permit and a minimum destruction and removal efficiency of 99.9999
percent for dioxin-bearing wastes F020, F021, F022, F023, F026, or F027 (§264.343(a)).
HYDROGEN CHLORIDE
HC1 is an acidic gas that forms when chlorinated organic compounds in hazardous
wastes are burned. An incinerator burning hazardous waste cannot emit more than 1.8
kg of HC1 per hour or more than 1 percent of the total HC1 in the stack gas prior to
entering any pollution control equipment, whichever is larger (§264.343(b)).
PARTICULATE MATTER
PM is tiny particles of ash that are carried along with the combustion gases to the
incinerator's stack. The incinerator regulations control metal emissions through the
performance standard for particulates, since metals are often contained in or attached to
the particulate matter. A limit of 180 milligrams of particulate matter per dry standard
cubic meter of gas emitted through the stack has been established in §264.343(c).
2.4 OPERATING CONDITIONS
The goal of setting operating conditions for hazardous waste incinerators is to ensure
compliance with the performance standards discussed in the previous section (i.e., for
organics, HC1, and PM). An incinerator permit specifies operating conditions that have
been shown in a trial burn to result in the incinerator meeting these performance
standards. A very important aspect of the regulations is that compliance with the
operating conditions specified in the permit is deemed to be compliance with the
performance standards for organics, HC1, and PM (§264.343(d)).
A RCRA permit for a hazardous waste incinerator sets operating conditions that specify
allowable ranges for, and requires continuous monitoring of, certain critical parameters.
Operation within these parameters ensures that combustion is performed in the most
protective manner and the performance standards are achieved. These parameters, or
operating conditions, include (264.345(b)):
• Maximum allowable carbon monoxide levels in stack emissions
• Allowable ranges for temperature
• Maximum waste feed rates
• Combustion gas velocity
The information in this document is not by any means a complete representation of EPA's regulations or policies,
but is an introduction to the topic used for Hotline training purposes.
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6 - Hazardous Waste Incinerators
• Limits on variations of system design and operating procedures.
In addition, during the start up and shut down of an incinerator, hazardous waste must
not be fed into the unit unless it is operating within the conditions specified in the
permit (§264.345(c)). An incinerator must cease operations when changes in waste feed,
incinerator design, or operating conditions exceed limits designated in its permit
(§264.345(f)).
FUGITIVE EMISSIONS
Operating conditions are also set to control fugitive emissions. Fugitive emissions are
gases that escape from the combustion chamber (for example, gases may escape
through the opening where wastes are fed into the combustion chamber) and do not
pass through pollution control devices. Fugitive emission control methods are (1)
maintaining negative pressure in the combustion zone so that air will be pulled into the
APCD rather than escaping into the ambient air, or (2) totally sealing the combustion
chamber so that no emissions can escape to the environment (§264.345(d)).
2.5 PERMIT PHASES
An owner/operator wishing to operate a new hazardous waste incinerator is required to
obtain a RCRA permit before construction of the unit commences.
The purpose of a hazardous waste incinerator permit is to allow a new hazardous
incinerator to establish conditions including, but not limited to, allowable waste feeds
and operating conditions that will ensure adequate protection of human health and the
environment. The incinerator permit covers four phases of operation: pre-trial burn,
trial burn, post-trial burn, and final operating conditions (§270.62).
PRE-TRIAL BURN
The pre-trial burn phase of the permit allows the incinerator to achieve a state of
operational readiness necessary to conduct the trial burn. The pre-trial burn permit
conditions are effective for the minimum time (not to exceed 720 hours) required to
bring the incinerator to a point of operational readiness to conduct a trial burn. This
phase is often referred to as the shakedown period.
TRIAL BURN
The trial burn can be seen as the "test drive" of the incinerator. It is the time when the
owner/operator will bring the unit up to operational readiness, monitor the key
operating conditions, and measure the emissions. The trial burn test conditions are
based on the operating conditions proposed by the permit applicant in the trial burn
The information in this document is not by any means a complete representation of EPA's regulations or policies,
but is an introduction to the topic used for Hotline training purposes.
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Hazardous Waste Incinerators - 7
plan submitted to EPA for evaluation. EPA establishes conditions in the permit
necessary to conduct an effective trial burn, meaning that the burn will be
representational of the incinerator's intended day-to-day operation and will yield
meaningful data for analysis.
POST-TRIAL BURN
The post-trial burn period is the time for EPA to evaluate all of the data that was
recorded during the incinerators trial burn. To allow the operation of a hazardous
waste incinerator following the completion of the trial burn, EPA establishes permit
conditions sufficient to ensure that the unit will meet the incinerator performance
standards. This post-trial burn period is limited to the minimum time required to
complete the sampling, analysis, data computation of trial burn results, and the
submission of these results to EPA.
FINAL OPERATING CONDITIONS
After reviewing the results of the trial burn, EPA will modify the permit conditions
again, as necessary, to ensure that the operating conditions of the incinerator are
sufficient to ensure compliance with incinerator standards and protection of human
health and the environment. Owners/operators of incinerators must comply with the
final permit conditions for the duration of the permit, or until the permit is modified.
DATA IN LIEU OF TRIAL BURN
While most incinerators must undergo a trial burn, it is possible for a facility to submit
extensive information in lieu of the trial burn (§270.19(c)). EPA believes that most
combustion units will need to conduct trial burns in order to develop operating
conditions that ensure compliance with the performance standards. Data submitted in
lieu of the trial burn, therefore, must originate from a unit with a virtually identical
design that will burn wastes under virtually identical conditions (i.e., located at the
same facility).
2.6 WASTE ANALYSIS
During operation, the owner/operator of an incinerator must conduct sufficient waste
analyses to verify that the waste feed is within the physical and chemical composition
limits specified in the permit. This analysis may include a determination of a waste's
heat value, viscosity, and content of hazardous constituents, including POHCs. Waste
analysis also comprises part of the trial burn permit application (§264.341). EPA
stresses the importance of proper waste analysis to ensure compliance with emission
limits.
The information in this document is not by any means a complete representation of EPA's regulations or policies,
but is an introduction to the topic used for Hotline training purposes.
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8 - Hazardous Waste Incinerators
2.7 MONITORING AND INSPECTIONS
The specific monitoring and inspection requirements for incinerators are found in
§264.347. The owner/operator must perform, at a minimum, the following functions
while incinerating hazardous waste:
• Monitor the combustion temperature, waste feed rate, and indicator of
combustion gas velocity on a continuous basis
• Monitor carbon monoxide on a continuous basis at a point downstream of the
combustion zone and prior to release into the atmosphere
• Sample and analyze the waste and exhaust emissions upon request of the
Regional Administrator to verify that the operating requirements established in
the permit achieve the performance standards
• Conduct daily visual inspections of the incinerator and associated equipment
• Test the emergency waste feed cut-off system and associated alarms at least
weekly unless otherwise directed by the Regional Administrator — at a
minimum operational testing must be conducted monthly
• Place monitoring and inspection data in the operating log.
2.8 MANAGEMENT OF RESIDUES
If an incinerator burns a listed hazardous waste, the ash is also considered a listed
waste. The derived-from rule states that any solid waste generated from the treatment,
storage, or disposal of a listed hazardous waste, including any sludge, spill residue, ash,
emission control dust, or leachate, remains a hazardous waste unless and until delisted
(§261.3(c)(2)(i)). The owner/operator must also determine whether the ash exhibits any
characteristics of a hazardous waste.
If an incinerator burns waste that only exhibits a characteristic of a hazardous waste, the
owner/operator must determine whether the ash exhibits any characteristics. Ash that
exhibits a characteristic must be managed as a hazardous waste.
2.9 CLOSURE
At closure, the owner/operator must remove all hazardous waste and hazardous
residues from the incinerator equipment site. In addition, as throughout the operating
period, if the residue removed from the incinerator is a hazardous waste, the owner or
operator becomes a generator of hazardous waste and must manage the residue in
The information in this document is not by any means a complete representation of EPA's regulations or policies,
but is an introduction to the topic used for Hotline training purposes.
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Hazardous Waste Incinerators - 9
accordance with the applicable requirements of Parts 262 through 266. (The module
entitled Closure/Post-Closure provides more detailed information on general
hazardous waste unit closure standards.)
2.10 COMPARISON OF PERMITTED AND INTERIM STATUS
INCINERATORS
The requirements for interim status incinerators are very similar to the already
discussed regulations for permitted units. The interim status regulations, however, are
designed to be self-implementing as the facilities are already in operation on the
effective date of the standards.
Figure 1 compares the requirements for permitted and interim status incinerators.
Figure 1
COMPARISON OF PARTS 264 AND 265
INCINERATOR REQUIREMENTS
PART 264, PERMITTED
PART 265, INTERIM STATUS
WASTE ANALYSIS
(§264.341)
Heating value
Viscosity
Appendix VIII
WASTE ANALYSIS
(§265.341)
Heating value
Waste halogen and sulfur content
Waste lead and mercury content
PERFORMANCE STANDARDS
(§264.343)
99.99% ORE for POHCs
99.9999% ORE for POHCs for dioxin-
bearing wastes
1.8 kg/hr or 1% HC1 emissions
180 mg/dscm PM
PERFORMANCE STANDARDS
(§§265.345 and 265.352)
Burn hazardous waste only during
steady state operations
99.9999% ORE and certification for
dioxin-bearing wastes
MONITORING & INSPECTIONS
(§264.347)
Combustion temperature
Waste feed rate
Combustion gas velocity
Carbon monoxide (CO)
Daily inspections
Weekly operations test
MONITORING & INSPECTIONS
(§265.347)
Monitor emission control system
every 15 minutes
Daily inspection
Daily operations test
The information in this document is not by any means a complete representation of EPA's regulations or policies,
but is an introduction to the topic used for Hotline training purposes.
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10 - Hazardous Waste Incinerators
CLOSURE
(§264.351)
Remove all hazardous waste and
residues
CLOSURE
(§265.351)
Remove all hazardous waste and
residues
In addition, the trial burn process for interim status incinerators is different than that
discussed previously in this module. As interim status units were already in operation
on the effective date of the regulations the facility would submit their trial burn plan for
approval without ceasing operation. Once this plan is approved, the facility would
conduct the trial burn test (or submit data in lieu of the trial burn) and continue
operating under interim status until the final permit is issued.
The information in this document is not by any means a complete representation of EPA's regulations or policies,
but is an introduction to the topic used for Hotline training purposes.
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Hazardous Waste Incinerators -11
3. REGULATORY DEVELOPMENTS
On April 19,1996, EPA published a proposed rule, called the "MACT" rule (maximum
achievable control technology), under the joint authority of RCRA and the Clean Air
Act (CAA), to upgrade the emission standards for hazardous waste combustors (61 FR
17358). Specifically, this rule will affect incinerators, cement kilns, and lightweight
aggregate kilns. It proposes emissions standards for dioxins, furans, mercury,
cadmium, lead, particulate matter, hydrochloric acid, chlorine, hydrocarbons, carbon
monoxide, and several low-volatile metals. EPA plans to address boilers and other
industrial furnaces in a future rulemaking. This rule fulfills EPA's commitment to
upgrade emissions standards as stated in its 1994 Strategy for Hazardous Waste
Minimization and Combustion.
On June 19,1998, EPA finalized the first phase of the MACT rule (63 FR 33782). This
final rule includes the comparable fuels exclusion and amendments to the permit
modification procedures for combustion facilities. EPA expects to finalize the
remainder of the April 19,1996, proposal in early 1999.
EPA expects that many combustion facilities currently operating under RCRA permits
will need to modify their permits in order to comply with the upcoming MACT
emissions standards. The current permit modification procedures are time consuming
and may hinder facilities from meeting the three-year compliance deadline established
by the CAA. To facilitate meeting the deadline, EPA revised the RCRA permit
modification procedures to explicitly address changes to a facility's design or
operations that are necessary to comply with the MACT standards (63 FR 33782,33801;
June 19,1998). EPA designated such changes as Class 1 modifications that require prior
Agency approval (see Permits and Interim Status module for further discussion of
permit modifications). EPA also incorporated a time default of 90 days, with a possible
one-time 30-day extension, for the permitting agency to make a decision about the
requested modification. If the agency fails to make a decision within the default time
frame, the permittee may consider the request approved. In authorized states, owners
and operators of facilities subject to the MACT standards will only be able to take
advantage of the revised permit modification procedures if the state has become
authorized for the revised modification provisions (see State Programs module for
further discussion of state authorization).
Interim status combustion facilities subject to the MACT standards will also have to
meet the three-year deadline. Interim status facilities are allowed to implement certain
facility changes if the changes do not amount to reconstruction (see Permits and Interim
Status module for further discussion of reconstruction). To ensure that the
reconstruction clause does not present an obstacle for interim status facilities trying to
implement changes to meet the new MACT emissions levels, EPA exempted changes
necessary to comply with the MACT standards from the reconstruction limit.
The information in this document is not by any means a complete representation of EPA's regulations or policies,
but is an introduction to the topic used for Hotline training purposes.
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12 - Hazardous Waste Incinerators
NOTICE OF INTENT TO COMPLY
EPA carefully considered public participation when promulgating the streamlined
permit modification procedures. In order to provide for public involvement early in a
source's compliance planning process, EPA requires owners and operators of
combustion facilities subject to the MACT standards to submit a Notification of Intent to
Comply (NIC) within one year of promulgation of the final standards indicating
whether the source intends to come into compliance with the new standards (63 FR
33782,33806; June 19,1998). In addition to submitting the NIC, EPA requires covered
facilities to provide notice of and host an informal meeting with the community to
discuss plans for complying with the MACT standards and to submit a progress report
within two years of promulgation of the final standards which demonstrates progress
made toward meeting the emissions standards.
WASTE MINIMIZATION AND POLLUTION PREVENTION
The CAA compliance deadline may cause companies to install simple end-of-pipe
emissions controls, instead of pollution prevention process changes. In order to limit
this practice and encourage waste minimization, EPA allows owners and operators of
combustion facilities to request a one-year extension to the MACT compliance period in
cases where additional time is needed to install pollution prevention and waste
minimization measures that reduce the amount of hazardous waste entering
combustion feedstreams (63 FR 33782,33816; June 19,1998). Requests for a one-year
extension must reasonably document that the waste minimization measures could not
be installed in time to meet the three-year compliance period. Decisions to grant the
extensions will be made by EPA or authorized state programs.
The rule proposes emissions standards for dioxins, furans, mercury, cadmium, lead,
particulate matter, hydrochloric acid, chlorine, carbon monoxide, hydrocarbons, and
several low volatile metals. It also proposes a new comparable fuels exclusion, and
makes significant changes to the existing combustion regulations.
EPA intends to finalize this proposal in two parts. The first part, expected in late 1997
or early 1998, is likely to include the comparable fuels exemption and the permit
modification amendments. The second part, expected later in 1998, will finalize the
remaining issues from the April 19,1996 proposal.
The information in this document is not by any means a complete representation of EPA's regulations or policies,
but is an introduction to the topic used for Hotline training purposes.
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Hazardous Waste Incinerators - 13
4. SPECIAL ISSUES
As EPA continues to revise the regulatory program for incinerators in order to
adequately protect human health and the environment, omnibus permitting authority,
site-specific risk assessments, and public participation issues have received greater
attention. The following discusses both issues in greater detail.
4.1 OMNIBUS PERMITTING AUTHORITY
The omnibus provision, added by Congress in the 1984 Hazardous and Solid Waste
Amendments, allows the Regional Administrator or state to incorporate into a permit
any provision deemed necessary to protect human health and the environment. EPA
codified this authority in §270.32(b)(2). Even if a facility submits a permit application
that is complete and technically adequate, if site-specific factors at the facility suggest
that typical permit conditions or performance standards will not assure protection of
human health and the environment, the Agency can impose additional conditions to
ensure such protection. Regulators can invoke the omnibus authority whenever a
facility owner/operator is seeking a new permit, reissue of an expiring permit, or when
existing permits are reopened for modification (in appropriate circumstances).
EPA has recommended that permit writers invoke the omnibus provision to more
stringently control emissions for toxic metals, HC1, and products of incomplete
combustion (PICs), and to enhance public participation in the combustion permitting
process. Also, under the Strategy for Hazardous Waste Minimization and Combustion,
EPA has directed states and regions to conduct site-specific risk assessments
(incorporating direct and indirect exposures) using the omnibus authority. These risk
assessments can be conducted by either the implementing agency or the facility (with
agency oversight) during the permitting process.
4.2 PUBLIC PARTICIPATION
On December 11,1995, EPA published a final rule expanding the role of public
participation in the RCRA permitting process. This rule affects incinerators by
increasing the extent of public participation during the trial burn process (60 FR 63417).
Specifically, the permitting agency is required to issue a public notice prior to
approving a facility's trial burn plan, and must announce the commencement and
completion dates for all trial burns. The proposed public participation rule (59 FR
28680; June 2,1994) also included some changes to the procedural requirements for
permitting interim status facilities. These changes, however, were not finalized because
of pending technical revisions to the hazardous waste combustor standards. See the
Regulatory Development section of this module for a discussion of this proposed rule.
The information in this document is not by any means a complete representation of EPA's regulations or policies,
but is an introduction to the topic used for Hotline training purposes.
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