

[Federal Register: January 18, 2007 (Volume 72, Number 11)]
[Proposed Rules]               
[Page 2219-2235]
From the Federal Register Online via GPO Access [wais.access.gpo.gov]
[DOCID:fr18ja07-25]                         

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ENVIRONMENTAL PROTECTION AGENCY

40 CFR Parts 261 and 302

[EPA-HQ-RCRA-2006-0984, FRL-8270-7]
RIN 2050-AG15

 
Hazardous Waste Management System: Identification and Listing of 
Hazardous Waste; Amendment to Hazardous Waste Code F019

AGENCY: Environmental Protection Agency (EPA).

ACTION: Proposed rule.

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SUMMARY: The Environmental Protection Agency (EPA) is proposing to 
amend today the list of hazardous wastes from non-specific sources 
(called F-wastes) under 40 CFR 261.31 by modifying the scope of the EPA 
Hazardous Waste No. F019 (Wastewater treatment sludges from the 
chemical conversion coating of aluminum except from zirconium 
phosphating in aluminum can washing when such phosphating is an 
exclusive conversion coating process). The Agency would be amending the 
F019 listing to exempt wastewater treatment sludges from zinc 
phosphating, when such phosphating is used in the motor vehicle 
manufacturing process. EPA is proposing two options that would require 
that the wastes be disposed in a landfill unit that meets certain liner 
design criteria. These proposed modifications to the F019 listing would 
not affect any other wastewater treatment sludges either from the 
chemical conversion coating of aluminum, or from other industrial 
sources. Additionally, this action would amend the Comprehensive 
Environmental Response, Compensation, and Liability Act (CERCLA) list 
of Hazardous Substances and Reportable Quantities under 40 CFR 302.4 so 
that the F019 listing description is consistent with the proposed 
amendment to F019 under 40 CFR 261.31.

DATES: Comments must be received on or before March 19, 2007. Under the 
Paperwork Reduction Act, comments on the information collection 
provisions must be received by OMB on or before February 20, 2007.

ADDRESSES: Submit your comments, identified by Docket ID No. EPA-HQ-
RCRA-2006-0984 by one of the following methods:
     http://www.regulations.gov: Follow the on-line instructions for 

submitting comments.
     E-mail: Comments may be sent by electronic mail (e-mail) 
to rcra.docket@epamail.epa.gov, Attention Docket ID No. EPA-HQ-RCRA-
2006-0984.
     Mail: Comments may be submitted by mail to: OSWER Docket, 
Office of Solid Waste, U.S. Environmental Protection Agency, Mailcode: 
5305T, 1200 Pennsylvania Avenue, NW., Washington, DC 20460, Attention 
Docket ID No. EPA-HQ-RCRA-2006-0984. Please include a total of three 
copies of your comments. In addition, please mail a copy of your 
comments on the information collection provisions to the Office of 
Information and Regulatory Affairs, Office of Management and Budget 
(OMB), Attn: Desk Officer for EPA, 725 17th Street, NW., Washington, DC 
20503.
     Hand Delivery: Deliver your comments to: EPA Docket 
Center, Public Reading Room, Room 3334, EPA West Building, 1301 
Constitution Avenue, NW., Washington, DC 20460, Attention Docket ID No. 
RCRA-2006-0984. Such deliveries are only accepted during the Docket's 
normal hours of operation (8:30 a.m. to 4:30 p.m., Monday through 
Friday, excluding legal holidays) and special arrangements should be 
made for deliveries of boxed information.
    Instructions: Direct your comments to Docket ID No. EPA-HQ-RCRA-
2006-0984. EPA's policy is that all comments received will be included 
in the public docket without change and may be made available online at 
http://www.regulations.gov, including any personal information provided, 

unless the comment includes information claimed to be Confidential 
Business Information (CBI) or other information whose disclosure is 
restricted by statute. Do not submit information that you consider to 
be CBI or otherwise protected through http://www.regulations.gov or e-mail. 

The http://www.regulations.gov Web site is an ``anonymous access'' system, 

which means EPA will not know your identity or contact information 
unless you provide it in the body of your comment. If you send an e-
mail comment directly to EPA without going through http://www.regulations.gov 

your e-mail address will be automatically captured and included as a 
part of the comment that is placed in the public docket and made 
available on the Internet. If you submit an electronic comment, EPA 
recommends that you include your name and other contact information in 
the body of your comment and with any disk or CD ROM you submit. If EPA 
cannot read your comment due to technical difficulties and cannot 
contact you for clarification, EPA may not be able to consider your 
comment. Electronic files should avoid the use of special characters, 
any form of encryption, and be free of any defects

[[Page 2220]]

or viruses. For additional information about EPA's public docket visit 
the EPA Docket Center homepage at http://www.epa.gov/epahome/dockets.htm
.

    Docket: All documents in the docket are listed in 
http://www.regulations.gov index. Although listed in the index, some 

information is not publicly available, i.e., CBI or other information 
whose disclosure is restricted by statute. Certain other material, such 
as copyrighted material, will be publicly available only in hard copy. 
Publicly available docket materials are available either electronically 
in http://www.regulations.gov or in hard copy at the OSWER Docket in the EPA 

Docket Center (EPA/DC), EPA West, Room 3334, 1301 Constitution Avenue, 
NW., Washington, DC 20460. The Public Meeting Room is open from 8:30 
a.m. to 4:30 p.m., Monday through Friday, excluding legal holidays. The 
telephone number for the OSWER Docket and the Public Reading Room is 
(202) 566-1744.

FOR FURTHER INFORMATION CONTACT: Mr. James Michael of the Office of 
Solid Waste (5304W), U.S. Environmental Protection Agency, 1200 
Pennsylvania Avenue, NW., Washington, DC 20460, (E-mail address and 
telephone number: michael.james@epa.gov, (703) 308-8610). For 
information on the procedures for submitting CBI data, contact Ms. 
LaShan Haynes (5305W), U.S. Environmental Protection Agency, 1200 
Pennsylvania Avenue, NW., Washington, DC 20460, (E-mail address and 
telephone number: haynes.lashan@epa.gov, (703) 605-0516).

SUPPLEMENTARY INFORMATION:

I. General Information

A. Who is Potentially Affected by This Proposed Rule?

    This regulation could directly affect businesses that generate 
certain wastes from the manufacturing of motor vehicles in the (1) 
automobile manufacturing industry and (2) light truck/utility vehicle 
manufacturing industry (NAICS codes 336111 and 336112, respectively). 
Other motor vehicle manufacturing industries (e.g., heavy duty truck or 
motor home manufacturing (NAICS code 336120)) are not affected by this 
rule. The wastes affected by this proposed rule are wastewater 
treatment sludges generated from the chemical conversion coating of 
aluminum using a zinc phosphating process and are currently listed as 
EPA Hazardous Waste No. F019 (see 40 CFR 261.31). If the rule is 
promulgated in either of the two ways it is proposed today, these 
wastes would not be hazardous waste, provided the wastes are disposed 
in a landfill unit that meets certain liner design criteria. Impacts on 
potentially affected entities are summarized in Section VI of this 
Preamble. The document, ``Estimate of Potential Economic Impacts for 
USEPA's Proposed Amendment to RCRA Hazardous Wastecode F019 to Exclude 
Motor Vehicle Manufacturing Industries,'' presents an analysis of 
potentially affected entities (hereinafter, referred to as the 
Economics Background Document). This document is available in the 
docket established in support of today's proposed rule. Entities 
potentially affected by this action are at least 14 current generators 
within the motor vehicle manufacturing industry consisting of six auto 
and eight light truck/utility vehicle plants and up to 39 other 
facilities in these two industries that may begin applying aluminum 
parts and could potentially generate F019 waste.
    To determine whether your facility is affected by this action, you 
should examine 40 CFR Parts 260 and 261 carefully, along with the 
proposed regulatory language amending Chapter I of the Code of Federal 
Regulations (CFR). This language is found at the end of this Federal 
Register notice. If you have questions regarding the applicability of 
this action to a particular entity, consult the person listed in the 
preceding section entitled FOR FURTHER INFORMATION CONTACT.

B. What Should I Consider as I Prepare My Comments for EPA?

    1. Submitting CBI. Do not submit this information to EPA through 
http://www.regulations.gov or e-mail. Clearly mark the part or all of the 

information that you claim to be CBI. For CBI information submitted on 
a disk or CD ROM that you mail to EPA, mark the outside of the disk or 
CD ROM as CBI and then identify electronically within the disk or CD 
ROM the specific information that is claimed as CBI. In addition to one 
complete version of the comment that includes information claimed as 
CBI, a copy of the comment that does not contain the information 
claimed as CBI must be submitted for inclusion in the public docket. 
Information so marked will not be disclosed except in accordance with 
the procedures set forth in 40 CFR part 2.
    2. Tips for Preparing your Comments. When submitting comments, 
remember to:
     Identify the rulemaking by docket number and other 
identifying information (subject heading, Federal Register date and 
page number).
     Follow directions--The agency may ask you to respond to 
specific questions or organize comments by referencing a Code of 
Federal Regulations (CFR) part or section number.
     Explain why you agree or disagree; suggest alternative and 
substitute language for your requested changes.
     Describe any assumptions that you used and provide any 
technical information and/or data that you used.
     If you estimate potential burden or costs, explain how you 
arrived at your estimate in sufficient detail to allow for it to be 
reproduced.
     Provide specific examples to illustrate your concerns and 
suggest alternatives.
     Explain your views as clearly as possible, avoiding the 
use of profanity or personal threats.
     Make sure to submit your comments by the comment period 
deadline identified.

Preamble Outline

I. Legal Authority
II. List of Acronyms
III. Overview
    Purpose of This Proposed Rule
IV. Background
    A. How EPA Regulates Hazardous Waste
    B. Overview of the F019 Listing
    C. Regulatory History of F006/F019
    D. Description of the Zinc Phosphating-Conversion Coating 
Process at Motor Vehicle Manufacturing Plants
    E. Amount of F019 Sludge Generated by the Motor Vehicle 
Manufacturing Industry
    F. Composition of the F019 Sludge
    G. How F019 Sludge Is Currently Managed
V. Approach Used in This Proposed Listing Amendment
    A. Concentration-Based Approach vs. Disposal in a Landfill 
Meeting Certain Liner Design Criteria
    B. Overview of the Risk Assessment
    1. EPA's Approach To Assessing Potential Risks to Human Health 
and the Environment
    2. How EPA Chose Constituents of Potential Concern for 
Evaluation
    3. Evaluation of Potential Human Health and Environmental Risks
    4. Uncertainty in the Risk Assessment Results
VI. Implementation of the F019 Proposed Rule
    A. Land Disposal Conditions
    1. How Generators Document Compliance With the Landfill 
Condition
    2. Consequences of Failing To Meet the Disposal Conditions and 
Recordkeeping Requirements
    3. Land Disposal Restrictions
    B. Interrelationships Between Proposed Rule and Current F019 
Delistings
VII. State Authorization
VIII. Comprehensive Environmental Response, Compensation, and 
Liability Act (CERCLA) Designation and List of Hazardous Substances 
and Reportable Quantities
IX. Relationship to Other Rules--Clean Water Act

[[Page 2221]]

X. Statutory and Executive Order Reviews
    A. Executive Order 12866: Regulatory Planning and Review
    B. Paperwork Reduction Act
    C. Regulatory Flexibility Act
    D. Unfunded Mandates Reform Act
    E. Executive Order 13132: Federalism
    F. Executive Order 13175: Consultation and Coordination With 
Indian Tribal Governments
    G. Executive Order 13045: Protection of Children From 
Environmental Health and Safety Risks
    H. Executive Order 13211: Actions That Significantly Affect 
Energy Supply, Distribution, or Use
    I. National Technology Transfer and Advancement Act
    J. Executive Order 12898: Federal Actions To Address 
Environmental Justice in Minority Populations and Low-Income 
Populations

I. Legal Authority

    EPA proposes these regulations under the authority of Sections 2002 
and 3001(b) and (f), 3004(d)-(m) and 3007(a) of the Solid Waste 
Disposal Act, as amended by the Resource Conservation and Recovery Act 
(RCRA), as amended, most importantly by the Hazardous and Solid Waste 
Amendments of 1984 (HSWA), 42 U.S.C. 6912, 6921(b), 6924(d)-(m) and 
6927(a). These statutes combined are commonly referred to as the 
``Resource Conservation and Recovery Act'' (RCRA) and will be referred 
to as such for the remainder of this Notice.
    Because EPA is modifying the national listing of F019, EPA believes 
the appropriate statutory authority is that found in section 3001 (b), 
rather than the authority in section 3001 (f). RCRA section 3001 (f) 
pertains solely to the exclusion of a waste generated at a particular 
facility in response to a petition. Accordingly, neither the procedures 
nor the standards established in that provision, or in EPA's 
regulations at 40 CFR 260.22 are applicable to this rulemaking.
    Section 102(a) of the Comprehensive Environmental Response, 
Compensation, and Liability Act of 1980 (CERCLA), 42 U.S.C. 9602(a) is 
the authority under which the CERCLA aspects of this rule are 
promulgated.

II. List of Acronyms

                                Acronyms
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         Acronym                             Definition
------------------------------------------------------------------------
BRS......................  Biennial Reporting System
CBI......................  Confidential Business Information
CERCLA...................  Comprehensive Environmental Response,
                            Compensation, and Liability Act
CFR......................  Code of Federal Regulations
COPCs....................  Constituents of Potential Concern
CWA......................  Clean Water Act
DAF......................  Dilution and Attenuation Factor
DRAS.....................  Delisting Risk Assessment Software
EPA......................  Environmental Protection Agency
ICR......................  Information Collection Request
IWEM.....................  Industrial Waste Management Evaluation Model
LDR......................  Land Disposal Restrictions
MCL......................  Maximum Contamination Limit
NAICS....................  North American Industrial Classification
                            System
NTTAA....................  National Technology and Transfer Act
OMB......................  Office of Management and Budget
OSWER....................  Office of Solid Waste and Emergency Response
PRA......................  Paperwork Reduction Act
POTW.....................  Publicly Owned Treatment Works ppm parts per
                            million
RCRA.....................  Resource Conservation and Recovery Act
RFA......................  Regulatory Flexibility Act
RQ.......................  Reportable Quantity
SIC......................  Standard Industrial Classification
TRI......................  Toxics Release Inventory
UMRA.....................  Unfunded Mandates Reform Act
WWT......................  Wastewater Treatment
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III. Overview

 Purpose of the Proposed Rule

    The Agency is proposing to amend the list of hazardous wastes from 
non-specific sources under 40 CFR 261.31 by modifying the scope of EPA 
Hazardous Waste No. F019, which currently reads: ``Wastewater treatment 
sludges from the chemical conversion coating of aluminum except from 
zirconium phosphating in aluminum can washing when such phosphating is 
an exclusive conversion coating process.'' The Agency is proposing to 
amend the F019 listing to exempt the wastewater treatment sludge 
generated from zinc phosphating, when zinc phosphating is used in the 
automobile assembly process and provided the waste is disposed in a 
landfill unit subject to certain liner design criteria. Specifically, 
under the two options proposed today, these wastes would not be 
hazardous if they are disposed in a landfill unit subject to, or 
otherwise meeting, certain liner requirements. Wastes that meet this 
condition would be exempted from the listing from their point of 
generation, and would not be subject to any RCRA Subtitle C management 
requirements for generation, storage, transport, treatment, or disposal 
(including the land disposal restrictions). Generators of such wastes 
may be exempted from the F019 listing if they meet the condition for 
exemption, and they maintain adequate records. EPA is proposing to 
require generators to keep records showing that they used a landfill 
that meets the design requirements.
    The motor vehicle manufacturing industry incorporates aluminum into 
vehicle parts and bodies for the purpose of making them lighter-weight 
and thus more capable of increasing gas mileage. However, when aluminum 
is incorporated into the body of an automobile, the conversion coating 
step in the manufacturing process results in the generation of a RCRA-
listed hazardous waste (F019) in the form of a wastewater treatment 
sludge from the

[[Page 2222]]

conversion coating process, while the wastewaters from the conversion 
coating of steel in the same industry do not generate a listed 
hazardous waste. By removing the regulatory controls under RCRA, EPA is 
facilitating the use of aluminum in motor vehicles. The Agency believes 
that the incorporation of aluminum will be advantageous to the 
environment since lighter-weight vehicles are capable of achieving 
increased fuel economy and associated decreased exhaust air emissions.

IV. Background

A. How EPA Regulates Hazardous Waste

    EPA's regulations establish two ways of identifying solid wastes as 
hazardous under 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 the Agency 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, and toxicity (see 40 CFR 261.21-
261.24). As a generator, you must determine whether or not a waste 
exhibits any of these characteristics by testing, or by using your 
knowledge of the process that produced the waste (see Sec.  262.11(c)).
    EPA may also conduct a more specific assessment of a waste or 
category of wastes and ``list'' them if they meet criteria set out in 
40 CFR 261.11. Under the third criterion, identified in 40 CFR 261.11 
(a)(3), the Agency may list a waste as hazardous if it contains 
hazardous constituents identified in 40 CFR part 261, Appendix VIII, 
and if EPA concludes that ``the waste is capable of posing a 
substantial present or potential hazard to human health or the 
environment when improperly treated, stored, transported, or disposed 
of, or otherwise managed.'' EPA places chemicals on the list of 
hazardous constituents in Appendix VIII ``if they have been shown in 
scientific studies to have toxic, carcinogenic, mutagenic or 
teratogenic effects on humans or other life forms.'' See 40 CFR 
261.11(a)(3). When listing a waste, the Agency also adds any hazardous 
constituents that serve as the basis for listing the waste to 40 CFR 
part 261, Appendix VII.
    The regulations at 40 CFR 261.31 through 261.33 contain the various 
hazardous wastes the Agency has listed to date. Section 261.31 lists 
waste generated from non-specific sources, known as ``F-wastes,'' and 
contain wastes that are usually generated by various industries or 
types of facilities. Today's proposed regulations would revise the 
listing for one of these wastes, F019.
    If a waste exhibits a hazardous characteristic, or is listed as a 
hazardous waste, then it is subject to federal requirements under RCRA. 
Facilities that generate, transport, treat, store or dispose of such 
waste must meet hazardous waste management requirements, including the 
need to obtain permits to operate, are commonly referred to as 
``Subtitle C'' facilities. (Subtitle C is the subsection of RCRA that 
governs the management of hazardous waste. EPA standards and procedural 
regulations implementing Subtitle C are found generally at 40 CFR parts 
260 through 273.)
    The RCRA regulations provide a form of relief for listed wastes 
through a site-specific process known as ``delisting.'' The regulations 
governing the delisting process are given at 40 CFR 260.20 and 260.22. 
These regulations set out a procedure and standards by which persons 
may demonstrate that a specific waste from a particular generating 
facility should not be regulated as a listed hazardous waste under 
Subtitle C of RCRA. Under these regulations, any person may petition 
EPA to remove its waste from regulation by excluding it from the lists 
of hazardous wastes contained in Part 261. EPA has granted delistings 
to various facilities that generate or manage F019 wastes, including 
motor vehicle manufacturing plants. (See Section IV.D.) As a condition 
to some of the granted delistings, the facility generating that waste 
must periodically sample and analyze the waste for the presence and 
quantity of specific chemical constituents of concern. This periodic 
sampling and analysis is called ``verification sampling.'' In some 
cases, facilities submit the results of the verification sampling and 
analysis to EPA to ensure that the waste's continuing status of 
nonhazardous is appropriate.
    A solid waste, that is determined not to be a listed and/or 
characteristic hazardous waste, may be managed at ``Subtitle D'' 
facilities. These facilities are approved by state and local 
governments and generally impose less stringent requirements on 
management of wastes than Subtitle C facilities. Subtitle D is the 
statutory designation for that part of RCRA that deals with disposal of 
nonhazardous solid waste. EPA regulations affecting Subtitle D 
facilities are found at 40 CFR parts 240 through 247, and 255 through 
258. Regulations for Subtitle D landfills that accept municipal waste 
(``municipal solid waste landfills'') are in 40 CFR part 258.

B. Overview of F019 Listing

    Hazardous Waste No. F019 is defined as ``Wastewater treatment 
sludges from the chemical conversion coating of aluminum except from 
zirconium phosphating in aluminum can washing when such phosphating is 
an exclusive conversion coating process.'' The hazardous constituents 
for which the waste is listed are hexavalent chromium and cyanide 
(complexed). The F019 wastewater treatment sludge is generated from the 
rinses and overflows from the chemical conversion coating of aluminum. 
Chemical conversion coating processes involve the application of a 
coating to a previously deposited metal or a base metal for increased 
corrosion protection, lubricity, preparation of the surface for 
additional coatings, or formulation of a special surface appearance. 
This manufacturing operation includes chromating, phosphating, metal 
coloring and immersion plating.
    Phosphate conversion coatings produce a mildly protective layer of 
insoluble crystalline phosphate on the surface of a metal. Phosphate 
coatings are used to provide a more suitable base for paints and other 
inorganic coatings, to condition the surfaces for cold forming 
operations by providing a base for drawing compounds and lubricants, 
and to impart corrosion resistance to the metal surface by the coating 
itself or by providing a suitable base for rust-preventive oils or 
waxes. Phosphate conversion coatings are formed by the immersion of 
iron, steel or zinc plated steel in a dilute solution of phosphoric 
acid plus other reagents. Phosphate conversion coatings can also 
involve spray-on applications.

C. Regulatory History of F006/F019

    On May 19, 1980, EPA published an interim final rule listing 
``wastewater treatment sludges from electroplating operations'' as EPA 
Hazardous Waste No. F006. See 40 CFR 261.31 (45 FR 33112). The 
hazardous constituents for which this waste was listed are cadmium, 
hexavalent chromium, nickel and complexed cyanide. In response to 
comments on the interim final regulation, the listing was modified on 
November 12, 1980 (45 FR 74884) to read as follows: ``wastewater 
treatment sludges from electroplating operations except from the 
following processes: (1) Sulfuric acid anodizing of aluminum; (2) tin 
plating on carbon steel; (3) zinc

[[Page 2223]]

plating (segregated basis) on carbon steel; (4) aluminum or zinc-
aluminum plating on carbon steel; (5) cleaning/stripping associated 
with tin, zinc and aluminum plating on carbon steel; and, (6) chemical 
etching and milling of aluminum.''
    Additionally, in response to other comments, the Agency separated 
``wastewater treatment sludges from the chemical conversion coating of 
aluminum'' from the F006 listing and listed them as F019. Commenters 
had argued that these sludges should not be listed as F006 because they 
do not contain all four of the constituents for which F006 was listed. 
That is, commenters contended that these wastes do not typically 
contain cadmium and nickel. EPA agreed that these wastes did not 
typically contain cadmium and nickel, but maintained that, since the 
wastes contain hexavalent chromium and complexed cyanides, they should 
nevertheless be regulated. The Agency, therefore, listed them as 
hazardous waste, F019, and only listed hexavalent chromium and 
complexed cyanides as the constituents of concern for these wastes in 
Appendix VII of Part 261.\1\
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    \1\ Note that aluminum conversion coating using the zinc 
phosphating process utilizes nickel, as noted in section IV.D.; 
thus, nickel is a potential constituent of concern in the waste at 
issue in this proposed amendment.
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    On December 2, 1986 (51 FR 43350), EPA issued an interpretive rule 
stating that the Agency had re-evaluated its previous interpretations 
of the scope of the application of F006 and had determined that those 
interpretations were overly broad. As a result, the Agency stated that 
the following processes were not included in the F006 listing: chemical 
conversion coating, electroless plating and printed circuit board 
manufacturing. EPA further clarified that the F006 listing includes 
wastewater treatment sludges from: (1) Common and precious metals 
electroplating, except tin, zinc (segregated basis), aluminum and zinc 
plating on carbon steel; (2) anodizing, except sulfuric acid anodizing 
of aluminum; (3) chemical etching and milling, except when performed on 
aluminum; and, (4) cleaning and stripping, except when associated with 
tin, zinc, and aluminum plating on carbon steel. While this 
interpretation removed chemical conversion coating from the scope of 
F006, it did not affect the F019 listing. That is, wastewater treatment 
sludges from the chemical conversion coating of aluminum continued to 
be regulated as F019.
    Through a number of delistings and the Agency's evaluation for 
today's proposal, EPA has since learned that one of the chemical 
conversion coating operations--zinc phosphating--may not result in the 
generation of a hazardous wastewater treatment sludge. (See discussion 
below describing the zinc phosphating process.) Therefore, EPA is 
proposing today to amend the F019 listing to exempt the wastewater 
treatment sludges from zinc phosphating, when such phosphating is used 
at motor vehicle manufacturing plants, provided certain disposal 
conditions are met.
    EPA is not reopening any aspect of the F019 listing other than 
those specifically identified in this proposal, and will not respond to 
any comments that address issues beyond the specific proposals outlined 
in this notice.

D. Description of the Zinc Phosphating-Conversion Coating Process at 
Motor Vehicle Manufacturing Plants

    The zinc phosphating process at motor vehicle manufacturing plants 
is a multiple stage immersion process. The number of stages in the zinc 
phosphating process may vary from plant to plant, but they generally 
involve: cleaning and surface preparation, rinsing, conversion coating 
and rinsing.
    Cleaning and surface preparation: The purpose of this stage is to 
remove the physical contaminants from the surface of the assembled 
vehicle body so that the conversion coating will be applied evenly and 
continuously across the metal surfaces. Typical surface contaminants 
are metal working oil, rust protection oil, dirt and oxides from 
corrosion. Since the surface of the metal becomes part of the coating, 
this stage is particularly important. Improper processing can result in 
blisters or poor appearance in the metal finish. Cleaning and surface 
preparation is typically done first with water and surfactants followed 
by an alkaline solution. The alkaline solution removes microscopic 
layers of metal to ensure that metal is exposed and available for the 
chemical conversion reactions.
    Rinsing: The rinse stage stops the metal removal by washing away 
the alkaline solution. Rinsing is done with water followed by an 
alkaline rinse conditioner, which prepares the metal surface for the 
conversion coating process.
    Conversion coating: During this stage, the conversion coating 
process converts the metal surface of the assembled vehicle bodies by 
dissolving the metal and forming ``sites'' into which the zinc 
phosphate coating is deposited. The zinc phosphate coating provides a 
stable, corrosion resistant base for painting. The phosphated 
conversion coating bath contains phosphoric acid with certain metals 
(zinc and manganese) and accelerators such as nickel. Fluoride is added 
to control crystal structure and maintain the composition of the bath. 
Hexavalent chromium and complexed cyanides are not used in this zinc 
phosphating conversion coating process.\2\
---------------------------------------------------------------------------

    \2\ The analytical data for sludge samples show the presence of 
chromium and cyanide. Chromium appears to arise, in part, from the 
use of trivalent chromium in ``sealing'' during the rinsing step in 
the process; the source of trace levels of cyanide is not clear. 
However, levels of hexavalent chromium and cyanide were not present 
at levels of concern based on EPA's risk assessment (i.e., the 
``Technical Support Document: Assessment of Potential Risks from 
Managing F019 Waste from Motor Vehicle Manufacturing Industry'' in 
the docket for this proposed rulemaking); also see Section V.B.
---------------------------------------------------------------------------

    Rinsing: Once the conversion coating process is completed, the 
assembled vehicle bodies go through a water rinse to stop the 
conversion coating process and to remove any excess salts from the 
metal surfaces. A final acidic rinse is then used to seal the pores in 
the zinc phopshate coating and to remove any excess materials from the 
metal surfaces. During this final rinse, a sealant is added for 
additional corrosion protection. From here, the assembled vehicle 
bodies then proceed to the painting process.

E. Amount of F019 Sludge Generated by the Motor Vehicle Manufacturing 
Industry

    As of 2003, 11 automobile manufacturing plants (NAICS 336111) 
generated a total of 5,300 tons per year of F019 sludge ranging between 
177 and 1,249 tons per year per plant (average of 477 tons per year per 
plant), and 12 light truck/utility vehicle manufacturing plants (NAICS 
336112) generated a total of 9,300 tons per year of F019 sludge ranging 
between 112 to 1,620 tons per year per plant (average of 772 tons per 
year per plant). As of year-end 2005, EPA regional offices have 
delisted 47 former F019 generators in 19 industries, including 35,000 
cubic yards (i.e., about 35,000 tons) per year of F019 sludge formerly 
generated by 15 motor vehicle manufacturing plants. Historically, 
between 1995 and 2003, the annual count of F019 generators in the motor 
vehicle manufacturing industries affected by this proposed rule has 
fluctuated between 10 to 22 generators, and between 8,000 to 13,000 
tons per year of F019 sludge generated.

F. Composition of the F019 Sludge

    The F019 sludge from motor vehicle manufacturers is generated from 
dewatering of wastewater, typically

[[Page 2224]]

yielding a pressed ``filter cake'' with a solids content that ranges 
between 30% and 50% by weight. Reviewing the Material Safety Data 
Sheets for the chemicals used in, and prior to, the conversion coating 
process indicates that a wide range of elements can be expected to be 
present in the wastewaters and the sludges resulting from wastewater 
treatment.
    The specific chemical constituents that are found in motor vehicle 
manufacturers' F019 sludge, listed in order of frequency found, are 
nickel, fluoride, zinc, barium, copper and chromium (all found in 100% 
of a selected number of samples reviewed); tin, formaldehyde, lead, 
cobalt, mercury, sulfide and xylenes (found in 70-99% of a selected 
number of samples reviewed); acrylamide, vanadium, arsenic, cyanide, 
hexavalent chromium, and ethylbenzene (found in 50-69% of a selected 
number of samples reviewed).

G. How F019 Sludge Is Currently Managed

    According to data from the 2003 RCRA Hazardous Waste Biennial 
Report (http://www.epa.gov/enviro/html/brs/brs_query.html), F019 

sludges generated by motor vehicle manufacturers are disposed in RCRA 
Subtitle C regulated facilities, after de-watering, stabilization and/
or other treatment. Although two of the 17 generators in the motor 
vehicle manufacturing industry reportedly disposed their F019 sludges 
onsite (about 300 tons/year), all of the 22 automobile and light truck/
utility vehicle manufacturing plants in 2003 reported managing F019 
sludges offsite at RCRA Subtitle C regulated landfills in six states 
(IL, LA, MI, OK, PA, and SC), located at transport distances of 19 to 
1,500 miles (average 400 miles).
    EPA recognizes that several recent rulemakings related to RCRA-
listed hazardous wastes have proposed conditional exemptions from the 
regulatory definition of ``solid waste'' when such wastes, by virtue of 
their being recycled, are treated more as commodities than as wastes. 
For example, see 68 FR 61588, October 28, 2005. The Agency is not aware 
of any recycling or reclamation of F019 sludges; therefore, EPA 
believes that current market conditions do not support the recycling of 
F019 waste for the purposes of recovering the metal content of such 
waste. EPA requests comment on whether our understanding is accurate 
and whether recycling of F019 waste is economically feasible under 
today's market conditions. If recycling of F019 wastes becomes 
economically feasible or beneficial in the future, the Agency will 
consider its options for how to address this, including through a 
subsequent rulemaking, such as the ongoing rulemaking related to the 
definition of solid waste.

V. Approach Used in This Proposed Listing Amendment

A. Concentration-Based Approach vs. Disposal in a Landfill Meeting 
Certain Liner Design Criteria

    On April 22, 2005, EPA, through a posting on EPA's website, 
indicated that the Agency was in the process of considering a possible 
amendment to the F019 hazardous waste listing under RCRA. This possible 
amendment would have exempted waste water treatment sludges from the 
zinc phosphating processes at automotive assembly plants in the motor 
vehicle manufacturing industry when concentrations of constituents of 
concern in those wastes fell below risk-based exemption levels. On the 
F019 Web page, EPA provided waste sampling data and the methodology 
that the Agency would use in considering the revision of the F019 
listing using a concentration-based approach. Interested parties were 
invited to review and comment on the information collected to support 
the possible amendment that EPA was considering. The comment period for 
the web posting closed on June 1, 2005. Twelve comments were received. 
All commenters supported a revision to the F019 listing, although some 
expressed concern regarding testing conditions for potential chemicals 
of concern in the waste and how the concentration-based exemption would 
be structured. Copies of these comments are included in the docket for 
today's proposed rulemaking.
    Below in Section V. B., EPA presents a detailed discussion of the 
Agency's approach in assessing the potential risks to human health and 
the environment and how EPA chose the potential constituents of concern 
that could be used in the concentration-based approach. However, as the 
Agency conducted the risk analysis and developed the implementation 
schemes to go with this approach, several issues arose. First, a 
variety of issues arose related to establishing precise exemption 
concentrations for the waste, including: the amount of waste ultimately 
disposed in the modeled landfill (which is dependent on annual volume 
and years of disposal); which toxicity benchmarks to use (e.g., 
drinking water standards or other health-based values); and exposure 
assumptions built into the Delisting Risk Assessment Software (DRAS) 
model (e.g., groundwater consumption for different age groups). (See 
Section V. B. for a more detailed discussion on the documentation of 
the DRAS model.)
    Second, in order to accommodate the wide range in the volumes of 
F019 wastewater treatment sludges generated at the different automotive 
assembly plants, the Agency would need to develop different exemption 
levels for each of the constituents of concern for the various annual 
waste volumes (e.g., 500 cubic yards to 5000 cubic yards per year at 
500 cubic yard intervals). In order to ensure compliance with the 
concentration-based approach, the automotive assembly plants would need 
to maintain detailed records on the amount of waste generated and 
implement a representative sampling and analysis program to ensure that 
they met the exemption levels for the volume of waste each facility 
generated annually. Furthermore, two constituents were identified that 
presented potential risks to human health (arsenic and nickel) in an 
unlined landfill scenario as modeled by DRAS version 2. Rather than 
attempt to define precise exemption levels for constituents of concern, 
the Agency believes that it is simpler to require disposal in a 
landfill that is subject to certain liner design requirements. The 
Agency is proposing two options for the liner design requirements. 
Under option one, EPA is proposing that the landfill unit meet the 
liner requirements for municipal landfills in 40 CFR 258.40 or other 
liner designs containing a composite liner.\3\ Under option two, the 
Agency is proposing to allow disposal in state-permitted municipal 
solid waste landfills (subject to regulations in 40 CFR 258) and state-
permitted industrial solid waste landfills (subject to Federal 
regulations at 40 CFR 257), provided the landfill unit includes at 
least a single clay liner,\4\ and also in permitted hazardous waste 
landfills. This second option could ease implementation,

[[Page 2225]]

because the generator could rely on the state permitting agency to 
assure proper liner design. The Agency is seeking comment on this 
second approach, because the modeling results indicate that units with 
a less stringent liner design may also reduce the risk from the 
hazardous constituents of concern to acceptable levels.
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    \3\ As noted in Section V.B. below, the Federal regulations for 
municipal solid waste landfills require that new units (and lateral 
expansions of existing units) meet design criteria for composite 
liners and leachate collection systems (or other approved 
performance standards). A composite liner as defined in Sec.  258.40 
consists of a combination of a synthetic liner and an underlying 
compacted soil/clay liner. Disposal in hazardous waste landfills 
would also be allowed, because the regulations in Sec.  264.301 and 
Sec.  265.301 include composite liners.
    \4\ For this option, EPA assumes that single clay liners, even 
in older landfills, would meet the typical construction standards, 
i.e., the clay liner would have a low hydraulic conductivity (i.e., 
1 x 10-7 cm/sec) and be of sufficient thickness to ensure 
structural stability (i.e., 2 to 3 feet of compacted clay). EPA 
seeks comment on this assumption.
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    As discussed further below, EPA found that disposal of the waste 
under evaluation in such lined landfills would ensure protection of 
human health and the environment, without the need for testing and 
tracking of waste volume. EPA believes that the proposed approaches 
outlined in today's notice would be easier and less costly to implement 
than the concentration-based approach, but provides at least the same 
level of protection for human health and the environment.

B. Overview of the Risk Assessment

1. EPA's Approach To Assessing Potential Risks to Human Health and the 
Environment
    Today's action addresses a specific type of industrial sludge: 
sludge generated from the management of wastewaters generated at motor 
vehicle manufacturing (assembly) facilities. In general, industrial 
wastewater treatment sludges consist of suspended solids removed from 
wastewaters during treatment, which may involve various steps. As 
described in one delisting petition, for example, the treatment steps 
include: grit separation, pH adjustment to remove metals, addition of a 
coagulant, clarification to generate a dilute sludge, and dewatering of 
the sludge and grit solids via filter presses.\5\
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    \5\ See General Motors Corporation Oklahoma City Assembly Plant 
Delisting Petition for F019 Wastewater Treatment Plant Sludge Filter 
Cake, Section 3, Facility Operations in the docket.
---------------------------------------------------------------------------

    F019 sludges generated by the motor vehicle manufacturing 
industries are currently managed by onsite dewatering, followed by 
truck or rail shipment to offsite RCRA-permitted hazardous waste 
landfills. Because today's action proposes to allow disposal of the 
wastewater treatment sludge in landfills subject to, or meeting, 
certain design criteria, the Agency's risk assessment involved 
evaluating risks to human health and the environment from this landfill 
disposal scenario. (See the ``Technical Support Document: Assessment of 
Potential Risks from Managing F019 Waste from the Motor Vehicle 
Manufacturing Industry'' in the docket for this proposed rulemaking for 
a detailed description of the analysis that the Agency performed, 
hereinafter, referred to as the Technical Support Document.) EPA 
initially evaluated the potential risks posed by a hypothetical annual 
quantity of F019 waste that is disposed of in an unlined nonhazardous 
waste landfill, and then evaluated potential risks from disposal in 
landfills that use different liner technologies. The human health and 
environmental risk evaluation uses several environmental fate, 
transport, and exposure/risk models: Delisting Risk Assessment Software 
(DRAS), version 2.0,\6\ Tier 1 of the Industrial Waste Management 
Evaluation Model (IWEM),\7\ and EPA's Composite Model for Leachate 
Migration with Transformation Products (EPACMTP).\8\ These models have 
all been peer reviewed; see the Technical Support Document for a 
detailed description of the use of these models and their peer review.
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    \6\ ``RCRA Delisting Technical Support Document''. EPA906-D-98-
001. Interim Final. U.S. Environmental Protection Agency, Office of 
Solid Waste and Emergency Response, Office of Solid Waste. Prepared 
by U.S. Environmental Protection Agency, Region 6, Dallas, TX April 
2002.
    \7\ ``Industrial Waste Management Evaluation Model (IWEM) User's 
Guide.'' EPA530-R-02-013. U.S. Environmental Protection Agency, 
Office of Solid Waste and Emergency Response, Office of Solid Waste. 
Washington, D.C. August 2002, and ``Industrial Waste Management 
Evaluation Model (IWEM) Technical Background Document.'' EPA530-R-
02-012. U.S. Environmental Protection Agency, Office of Solid Waste 
and Emergency Response, Office of Solid Waste. Washington, DC August 
2002.
    \8\ ``EPA's Composite Model for Leachate Migration with 
Transformation Products EPACMTP: User's Guide.'' U.S. Environmental 
Protection Agency, Office of Solid Waste and Emergency Response, 
Office of Solid Waste. Washington, DC 1997, ``EPA's Composite Model 
for Leachate Migration with Transformation Products (EPACMTP) 
Technical Background Document.'' EPA530-R-03-006. U.S. Environmental 
Protection Agency, Office of Solid Waste and Emergency Response, 
Office of Solid Waste. Washington, DC April 2003, and ``EPA's 
Composite Model for Leachate Migration with Transformation Products 
(EPACMTP) Parameters/Data Background Document''. EPA530-R-03-003. 
U.S. Environmental Protection Agency, Office of Solid Waste and 
Emergency Response, Office of Solid Waste. Washington, DC April 
2003.
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    EPA's Regional Offices, and certain states, use version 2.0 of the 
DRAS model, or earlier versions of it, to determine whether to grant 
requests for delistings under 40 CFR 260.22. The DRAS model is a 
screening tool that contains several assumptions that are designed to 
be protective of public health. In addition, EPA then adjusted the DRAS 
model results to take into account exposures to children. The DRAS 
model assesses human health considerations, by assuming that 
populations that live near the landfill (nearby residents) may be 
exposed to chemical constituents that are released from the waste that 
is placed in the landfill. EPA used the DRAS model to calculate the 
levels of chemical constituents in a waste (waste concentrations) that 
would not exceed the acceptable levels at the nearby receptor. The 
acceptable levels are based on the target risks the Agency used in its 
evaluation. For carcinogens, EPA used an increased probability of 
developing cancer that is less than or equal to one in one hundred 
thousand (1 x 10-5). For non-carcinogens, EPA used a 
``hazard quotient'' less than or equal to 1.0; the hazard quotient is 
the ratio of an individual's chronic daily exposure to a standard, such 
as the chronic reference dose. (The reference dose is ``an estimate 
(with uncertainty spanning perhaps an order of magnitude) of a daily 
oral exposure for a chronic duration (up to a lifetime) to the human 
population (including sensitive subpopulations) that is likely to be 
without an appreciable risk of deleterious effects during a 
lifetime.'') \9\ These target risk levels are consistent with those 
discussed in EPA's hazardous waste listing determination policy (see 
the discussion in a proposed listing for wastes from the dye and 
pigment industries, December 22, 1994 (59 FR 66072)).
---------------------------------------------------------------------------

    \9\ See EPA's Integrated Risk Information System (IRIS) at 
http://www.epa.gov/iris/index.html.

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    The DRAS model assesses environmental risk by examining the aquatic 
organisms in a body of surface water downhill from the landfill 
(ecological receptors) that are exposed to small quantities of chemical 
constituents that are released from the waste in the landfill. As with 
the human health considerations, the Agency can assess an acceptable 
risk level for those aquatic organisms, such that the sustainability of 
the organisms' population in the surface water body is not compromised. 
The DRAS model then calculates the levels of chemical constituents in 
waste placed in the landfill (i.e., waste concentrations) that should 
not be exceeded in order to have acceptable levels of these 
constituents in the nearby body of surface water.
    For a landfill disposal scenario, the DRAS model predicts how 
constituents of potential concern, or COPCs, will move through the 
environment and affect nearby people or aquatic organisms. The DRAS 
model predicts releases of COPCs from the waste into the groundwater 
beneath the landfill, then accounts for human exposure from drinking 
contaminated groundwater, inhaling volatile constituents when using 
contaminated groundwater for showering, and dermal contact from bathing 
with contaminated groundwater. The DRAS model also

[[Page 2226]]

predicts releases of COPCs from the waste (both waste particles and 
volatile emissions) into the air above the landfill. DRAS then accounts 
for inhalation of volatile constituents and particles, and for 
windblown particles landing on soil and a child ingesting the 
contaminated soil. Finally, the DRAS model predicts releases of COPCs 
from the waste, due to storm water that erodes waste from an open 
landfill and runs off into a nearby body of surface water. Then the 
DRAS model takes into account human exposure from eating fish and 
drinking contaminated surface water, and for the exposures of the fish 
to contaminated surface water. In addition, EPA adjusted the DRAS model 
results to take into account exposures to children. See the Technical 
Support Document for a complete description of the scenario that is 
modeled in DRAS version 2.0, the human health and ecological exposure 
pathways, and the data sources the Agency used as model inputs. The 
DRAS version 2.0 technical documentation, ``User's Guide for the EPA 
Region 6 Delisting Risk Assessment Software'' (EPA906-D-98-001) and the 
``Delisting Technical Support Document,'' which is distributed as part 
of the DRAS modeling software, provides further details about the 
specific assumptions and the mathematical equations that the model 
uses. These documents are in the docket.
2. How EPA Chose Constituents of Potential Concern for Evaluation
    Section IV. F. describes briefly the constituents likely to be 
present in motor vehicle manufacturers' F019 waste. To identify 
constituents of potential concern, EPA reviewed information from 13 
motor vehicle manufacturing facilities' delisting petitions.\10\ This 
information included material safety data sheets (MSDS's) that identify 
the specific chemicals used in the conversion coating process; these 
chemicals are likely to be present in the wastewater that is treated 
and from which F019 sludge results.
---------------------------------------------------------------------------

    \10\ The 13 motor vehicle manufacturing facilities are BMWMC 
(BMW Manufacturing Corp.), located in Greer, South Carolina; Nissan, 
in Smyrna, Tennessee; General Motors (GM) in Lansing, Michigan; GM 
in Lake Orion, Michigan; GM in Oklahoma City, Oklahoma (draft 
petition submitted and available only in the EPA Headquarters docket 
for today's notice); GM in Lordstown, Ohio; GM in Pontiac, Michigan; 
GM in Hamtramck, Michigan; GM in Flint, Michigan; GM Grand River in 
Lansing, Michigan; Ford in Wixom, Michigan; Ford in Wayne, Michigan; 
and DaimlerChrysler Jefferson North in Detroit, Michigan.
---------------------------------------------------------------------------

    EPA also compiled the analytical data received from the 13 
facilities' delisting petitions (and from verification sampling at 
several facilities) into a spreadsheet that is available in the docket 
for this rulemaking. These 13 facilities analyzed F019 sludge samples 
for approximately 240 chemical constituents. Many chemicals were not 
found in the F019 sludge at the detection limits used. If these ``non-
detect'' chemicals were not mentioned on the material safety data 
sheets, then EPA did not evaluate these constituents further. For 
example, petitioners analyzed sludge samples for pesticides, such as 2-
sec-butyl-4,6-dinitrophenol (Dinoseb); however, these were not found in 
the MSDS's or in the sludge samples, nor would one expect to find them 
in a motor vehicle manufacturing facility's wastewater treatment 
sludge.
    Of the constituents analyzed in the F019 wastes, 56 were detected 
in one or more samples. EPA evaluated the concentrations reported by 
the petitioners for these 56 chemicals (including concentrations that 
laboratories reported as estimates). The Agency used the DRAS model 
methodology to evaluate potential risks for 55 detected constituents 
for human health risks and 49 for environmental risks.\11\
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    \11\ For human health, one constituent, sulfide, was not 
evaluated using the DRAS methodology because it lacks an appropriate 
toxicity value. For ecological risk, two constituents, sulfide and 
fluoride, were not evaluated using the DRAS methodology because they 
are not present in the DRAS version 2 data base for constituents, 
and lack appropriate toxicity values for environmental risks. For 
another five of the 56 constituents, EPA lacked appropriate aquatic 
toxicity benchmarks to complete an environmental risk assessment. 
See the Technical Support Document in the docket for this proposed 
rulemaking for details.
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3. Evaluation of Potential Human Health and Environmental Risks
    For both human health and environmental risk evaluations, EPA's 
analysis assumed the disposal of a total waste volume of 90,000 cubic 
yards of F019 into a landfill. This waste volume corresponds to either 
a 4,500 cubic yards per year disposal rate for 20 years, or a 3,000 
cubic yards per year disposal rate for 30 years. EPA believes it is 
quite unlikely that motor vehicle manufacturers would dispose of 
amounts greater than 90,000 cubic yards for an extended period of time 
in the same landfill based on a review of the delisting facilities' 
stated annual F019 sludge production quantities. EPA examined the 
information contained in the delisting petitions submitted and more 
recent data provided by facilities in the motor vehicle manufacturing 
industry. Combining the data from both sources for past generation of 
this waste, EPA found that the volumes of sludges disposed ranged from 
426 to 3,892 cy/yr (median was 1,088 cy/yr, and the 90th percentile 
ranked value was approximately 2,900 cy/yr). Therefore, the use of 
3,000 cubic yards per year or 4,500 cubic yards per year represents a 
protective upper-bound for the waste volumes reported by the generators 
and is likely to overestimate volumes currently produced by the 
automotive industry. A number of the constituents detected in the waste 
appear to be present at levels that may be of concern from a human 
health viewpoint. (None of the constituents that EPA evaluated for 
potential environmental harm appeared to be present at levels of 
concern.) When using the maximum detected concentrations and a total 
volume of 90,000 cubic yards disposed in a landfill, the DRAS modeling 
indicated that two of the 55 waste constituents evaluated for human 
health effects showed an estimated hazard quotient greater than 1, or 
showed an individual's estimated lifetime potential excess cancer risk 
to be greater than one in one hundred thousand.
    Based on the assessment using DRAS, the Agency determined that only 
two constituents (arsenic and nickel) had maximum detected values that 
exceeded the levels that DRAS modeling indicated would result in an 
acceptable exposure level. (The other constituents had estimated hazard 
quotients less than 1 and estimated individual lifetime excess cancer 
risk of less than one in one hundred thousand.) For nickel in 
groundwater used as drinking water, the estimated hazard quotient was 
three. For arsenic in groundwater used as drinking water, the estimated 
individual excess lifetime cancer risk was three in one hundred 
thousand. Thus, using protective exposure assumptions, the Agency found 
that disposing of a total of 90,000 cubic yards of waste (equivalent to 
3,000 cubic yards disposed per year for 30 years) containing these two 
constituents, at their maximum detected concentrations in an unlined 
landfill, exceeded the DRAS limit by up to a factor of 3. The Technical 
Support Document describes the DRAS modeling and results, with 
discussion and conclusions, in considerably greater detail.
    As described above, two constituents (arsenic and nickel) were at 
levels that may be of concern using upper-bound assumptions for waste 
quantities disposed and constituent concentrations in unlined 
landfills. Furthermore, the constituents were reported to be prevalent 
in the waste samples. Therefore, EPA examined the robustness of one of 
the key assumptions of the DRAS version 2.0 modeling--modeling

[[Page 2227]]

disposal in a landfill without a liner. Within the past 15 years, 
changes to landfill requirements in the United States (the promulgation 
of federal regulations that require municipal solid waste landfills to 
meet certain leakage prevention requirements, and requirements for 
collecting and managing landfill gases, e.g., see 40 CFR 258.40) have 
caused substantial changes in landfill practices. The majority of 
municipal solid waste landfills, and probably many landfills that 
accept nonhazardous industrial solid waste but not municipal solid 
waste, now are designed, built, and operated with liner systems that 
typically include composite liners and leachate collection systems (or 
other approved performance standards). The potential risks found by the 
DRAS version 2.0 modeling were all from groundwater exposure pathways. 
As a result, current landfills with liner systems and leachate 
collection systems should dramatically lessen impacts on local 
groundwater conditions.
    DRAS does not have an option to model the impact of liners on 
landfill releases. Therefore, to examine the potential impact of 
liners, the Agency compared the levels calculated by the Industrial 
Waste Management Evaluation Model (IWEM), for single-lined and 
composite-lined landfills.\12\ IWEM is the ground-water modeling 
component of the Guide for Industrial Waste Management, used for 
recommending appropriate liner system designs for the management of 
RCRA Subtitle D industrial waste. The initial IWEM evaluation (Tier 1) 
provides a screening assessment with results that are protective over a 
range of conditions and situations. The results of the IWEM analysis 
indicate that the use of a composite-lined landfill would result in 
acceptable risk levels for the two key constituents of concern. The 
IWEM generally uses more protective assumptions than the DRAS model. 
For example, the IWEM model assumes that the drinking water well is at 
a fixed location along the center line of the potential plume of 
contamination at a distance of 150 meters from the unit; the DRAS model 
allows the well location to vary downgradient from the unit.
---------------------------------------------------------------------------

    \12\ In IWEM, a single cay liner is a layer of compacted clay 
three feet thick (hydraulic conductivity of 1 x 10-7 cm/
sec), and a composite liner consists of a geomembrane liner (high 
density polyethylene) overlying the clay layer.
---------------------------------------------------------------------------

    To further examine the effectiveness of composite liners, EPA also 
used the modeling performed for lined landfills in the recent listing 
rule for dye and pigment production wastes (February 24, 2005, 70 FR 
9138). In this rule, the Agency established a conditional exemption for 
wastes disposed in landfills meeting specified liner design 
requirements, similar to the proposal in today's notice. The results 
from that effort show that composite-lined landfills provided 
significant protection (about two orders of magnitude) compared to an 
unlined unit.\13\ Therefore, based on both the IWEM results and the 
modeling in the dye and pigment waste listing, EPA believes that 
disposal of F019 sludges from motor vehicle manufacturers in composite-
lined landfills (or other approved performance standards) is protective 
of human health and the environment.
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    \13\ The results for zinc and several other metals (lead, 
copper, and barium) demonstrated that composite lined landfills 
reduced risks from landfill releases factors of 133 to 269 compared 
to unlined units. See ``Risk Assessment Technical Background 
Document for the Dye and Pigment Industry Hazardous Waste Listing 
Determination,'' November 10, 2003, Table 2-1b, page 2-4.
---------------------------------------------------------------------------

    The Agency also considered whether the presence of just a single 
clay liner would be sufficient to reduce the risks below levels of 
concern. In addition to the IWEM results that showed disposal in a 
composite-lined landfill was protective, this analysis also yielded 
levels that would be allowed for a landfill with a single clay liner 
and for an unlined landfill. For nickel, the levels that would be 
allowed for a single clay liner were approximately 3-fold higher than 
the allowable levels for an unlined unit. For arsenic, the allowable 
level for a single clay liner was approximately 7-fold higher than the 
allowable level for an unlined unit. Thus, a single clay liner (as 
defined in the IWEM model assumptions) may be sufficiently protective 
to allow disposal in a unit with such a single liner, because a single 
clay liner may reduce the risks from these constituents to levels below 
the DRAS levels of concern. (EPA is somewhat uncertain about the 
appropriateness of extending the apparent margin of safety afforded by 
a single clay liner from one model (IWEM) to another model's results 
(DRAS), and we are seeking comment on this approach.) Therefore, EPA is 
requesting comment on a second regulatory option that would allow 
disposal of this waste in all state-permitted municipal solid waste 
landfills (regulated under 40 CFR Part 258) and state-permitted 
industrial solid waste landfills (regulated under 40 CFR Part 257), 
even those that do not meet the liner design requirements in Sec.  
258.40, provided the landfills are equipped with at least a single clay 
liner.\14\ The second option, for example, would allow disposal in a 
state-permitted municipal landfill that was constructed prior to the 
effective date for the Sec.  258.40 regulations (an ``existing'' unit), 
provided the unit had at least a single clay liner. EPA expects that 
this would provide additional regulatory flexibility for generators, 
and would not be likely to result in adverse health effects.
---------------------------------------------------------------------------

    \14\ This second proposed option would also allow disposal in a 
hazardous waste landfill regulated under Sec.  264.301 or Sec.  
265.301, which require composite liner systems.
---------------------------------------------------------------------------

    Therefore, EPA is taking comment on a second option, which would 
allow disposal in a landfill with a single clay liner, as well as 
allowing disposal in landfills with the more protective composite liner 
systems. Under this option, the regulatory language for the F019 could 
be revised to read as follows.

    Wastewater treatment sludges from the manufacturing of motor 
vehicles using a zinc phosphating process will not be hazardous if 
the wastes are either: disposed in a Subtitle D municipal or 
industrial landfill unit that is equipped with a single clay liner 
and is permitted, licensed or otherwise authorized by the state; or 
disposed in a unit that is subject to, or otherwise meets, the liner 
requirements in Sec.  258.40, Sec.  264.301, Sec.  265.301.

    EPA is requesting comments on whether adequate clay liners are 
found in active older municipal landfill units and industrial solid 
waste landfills, and whether this requirement would provide any 
significant regulatory relief for generators by meaningfully expanding 
their disposal options. EPA is also seeking comment on the likelihood 
of generators of the F019 waste constructing landfill units at their 
facilities and what types of liner systems would be used for these 
onsite units. EPA also solicits comment on whether the option allowing 
disposal in a landfill unit with a clay liner (permitted or licensed by 
the state) will be straightforward to implement or whether it will 
raise implementation or compliance issues for the waste generator, such 
as the availability of state standards for clay liners in older 
landfills.
    The Agency is seeking comments on the level of regulatory relief 
that would be provided by both of these proposed approaches. Municipal 
landfills, for example, have been required to have composite liners (or 
performance based equivalents) as set out in 40 CFR 258.40, except for 
``existing'' units (i.e., generally units or cells that existed prior 
to 1993). Therefore, EPA believes that most lined landfill units are 
likely to have composite liners. The Agency is seeking information on 
the extent to

[[Page 2228]]

which generators would use the option of sending waste to units with 
only single clay liners (under proposed option two) and any information 
relevant to the existence and likely use of landfill units with single 
clay liners. In addition, EPA is seeking comments on the burden 
associated with the recordkeeping requirements that would result from 
documenting compliance with disposal of the exempt waste in a landfill 
unit with a single clay liner or a composite liner. Under the second 
proposed option, the generator would be required to document that the 
waste went to a permitted landfill unit that was equipped with a clay 
liner. In this case, however, the generator would be able to rely on 
the permitting agency to ensure that the clay liner was adequate. EPA 
solicits comments on any issues that might be raised by this approach 
to recordkeeping and documentation.
4. Uncertainty in the Risk Assessment Results
    The Technical Background Document describes the risk results, and 
gives examples of the known uncertainties associated with the risk 
results. The risk results used for this proposal are based on the same 
kinds of data and health protective models that the Agency typically 
uses in national-scale waste policy decision making. The risk results 
show estimated risks for an individual at the ``high-end'' of the risk 
distribution, and are designed to be protective of human health and the 
environment. As such, the resulting risk estimates are likely to 
reflect protective outcomes in more than 90 percent of the situations 
modeled.\15\ When using central tendency assumptions \16\ for an 
unlined landfill, the hazard quotient for nickel was calculated to be 
0.1 and the cancer risk factor for arsenic was two in a million, both 
values being well below the risk thresholds used by the Agency in 
hazardous waste listing determinations.
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    \15\ Conceptually, ``high-end'' means above the 90th percentile 
of the risk distribution; see Guidance on Risk Characterization for 
Risk Managers and Risk Assessors, February 26, 1992 memorandum from 
F. Henry Habicht, II, Deputy Administrator, to Assistant 
Administrators and Regional Administrators. We use the term ``high-
end'' here to refer to modeling inputs that are at or above the 90th 
percentile of a data set.
    \16\ Note that the results described as ``central tendency'' 
here reflect changes in annual waste volume, disposal time, and 
constituent concentration (and for non-cancer effects, drinking 
water intake). Other variables, such as the dilution/attenuation 
factor and exposure frequency (and for cancer effects, drinking 
water intake) remain at high-end values.
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    Our overall assessment is that the models we use could overestimate 
the potential adverse effects of disposing of the F019 waste in either 
unlined or lined landfills. Thus, actual exposures that would be 
experienced by future residents near the landfill will likely be lower 
than those estimated using the DRAS version 2 model. Examples of the 
protective assumptions used in the high-end DRAS results include: (1) 
The disposal volume (the 90th percentile value of 3,000 cubic yards per 
year in the same landfill for 30 years), (2) the constituent 
concentrations (the maximum values found in the sampling data from the 
13 delisting submissions), and (3) exposure levels (90th percentile 
value for ingestion of groundwater by children for 350 days per year).
    The risk results represent EPA's reasonable efforts in using 
existing knowledge of the national waste management system, the science 
of environmental fate and transport of chemicals, and the science of 
toxicology to assess the likely hazards of managing the F019 waste as 
nonhazardous. The Agency believes that, in spite of some of the 
specific uncertainties that exist, the risk estimates provide a useful 
basis for our decision about whether to continue to regulate this waste 
as a hazardous waste. EPA is requesting comments on our risk assessment 
approach and on the resulting risk estimates.

VI. Implementation of the F019 Proposed Rule

A. Land Disposal Conditions

    The proposed amendment to the F019 listing exempts certain wastes 
disposed in landfill units that are subject to certain liner design 
requirements. This exemption is based on EPA's risk analysis 
demonstrating that wastes disposed in landfills with certain types of 
liners do not present significant risks for sludges generated by motor 
vehicle manufacturers. Today's first proposal would allow motor vehicle 
manufacturers (as defined in Sec.  261.31(b)(i)) to manage wastes from 
chemical conversion coating of aluminum when using a zinc phosphating 
process as nonhazardous, if the wastes are disposed in a landfill 
subject to, or otherwise meeting, the landfill requirements in Sec.  
258.40, Sec.  264.301 or Sec.  265.301. The second proposal in today's 
notice would also exempt the waste if the generators dispose of the 
waste in a state-permitted non-hazardous landfill unit that has, at a 
minimum, a single clay liner.
    The requirements under Sec.  258.40, which apply to new municipal 
solid waste landfills or new units at existing municipal solid waste 
landfills, require use of a composite liner and leachate collection 
system (or a design meeting a protective performance standard and 
approved by the Director of an approved state program or by EPA). The 
infiltration rates used by IWEM (and also for the Dye and Pigment 
listing; 70 FR 9138, February 24, 2005) were based on data from 
landfills with composite liners similar to the design required under 
Sec.  258.40. Consequently, EPA's proposed option number one allows 
disposal of wastes in a municipal solid waste landfill unit that is 
subject to the Sec.  258.40 design requirements. EPA is specifying that 
the landfill unit must be subject to these requirements because some 
operating landfills may still use older units that are not required to 
meet the design requirements in Sec.  258.40. The Agency's risk 
assessment shows that unlined landfills may not be sufficiently 
protective for some of the sludges from automobile manufacturing, i.e., 
higher volume sludges with high levels of key constituents of concern. 
Federal law requires that all municipal landfills comply with the Part 
258 landfill regulations. Additionally, states have permitting programs 
to implement the Part 258 requirements for municipal landfills. Permit 
programs must ensure that municipal landfill units in the states comply 
with the Sec.  258.40 design standards (see 40 CFR 239.6(e)). 
Consequently, landfill cells subject to the Part 258.40 design 
standards are required to comply with the federal standards or more 
stringent state standards.
    Some generators of F019 wastes may still choose to send wastes to 
Subtitle C hazardous waste landfills. New landfill units and lateral 
expansions of existing hazardous waste landfills are required to have 
``double'' composite liners including synthetic components. See 40 CFR 
264.301 and 265.301. The Agency would expect that these liner systems 
have even lower infiltration rates than the composite liners required 
under Sec.  258.40, because the Subtitle C requirements include another 
composite liner, in addition to the composite liner (or equivalent) 
required of municipal solid waste landfills (e.g., see Sec.  
261.301(c)). Therefore, EPA is proposing to give generators the option 
of sending wastes to landfill units subject to these stricter hazardous 
waste liner requirements.
    The Agency is also proposing to include a third class of landfills 
in the exemption, namely, Subtitle D industrial solid waste landfills 
that meet the liner design requirements in Sec.  258.40 or Subtitle C 
landfills. These ``industrial landfills'' are subject to Federal 
regulations in Part 257, which apply to non-municipal, nonhazardous 
waste landfills. While the Part 257

[[Page 2229]]

regulations do not have liner requirements, states have regulations 
governing the design of such landfills that often include requirements 
for liner systems.\17\ EPA believes that generators should have the 
option of using lined industrial landfills that are as protective as 
lined municipal solid waste landfills.
---------------------------------------------------------------------------

    \17\ Commercial offsite landfills are subject to regulations by 
states, including liner requirements. See the report by Association 
of State and Territorial Solid Waste Management Officials (ASTSWMO), 
``Non-Municipal, Subtitle D Waste Survey,'' March 1996, and the EPA 
report, ``State Requirements for Industrial Non-Hazardous Waste 
Management Facilities,'' October 1995.
---------------------------------------------------------------------------

    Therefore, under the first option, EPA is proposing that the 
amended listing include an exemption for wastes disposed in any 
landfill that is subject to, or meets, the landfill requirements in 
Sec.  258.40, Sec.  264.301, or Sec.  265.301. Under the second option, 
EPA is proposing an alternative approach that would also allow disposal 
of the subject waste in a landfill unit with a single clay liner as 
described previously.
    Note, however, that this exemption would not apply if wastewaters 
from aluminum conversion coating processes using the zinc phosphating 
process are commingled with wastewaters arising from aluminum 
conversion coating using other non-exempt processes (e.g., chromating 
processes); the sludge resulting from such commingled wastewaters would 
still carry the F019 waste code, because it would be derived, in part, 
from an aluminum conversion coating process that is not zinc 
phosphating. Furthermore, aluminum conversion coating sludges derived 
from zinc phosphating at motor vehicle manufacturers are still subject 
to the ``mixture rule,'' and would become hazardous waste if mixed with 
any other listed hazardous waste.\18\ In addition, the motor vehicle 
manufacturers would also be subject to the requirements of Sec.  268.3 
(dilution prohibited as a substitute for treatment). Finally, if the 
zinc phosphating sludges were generated such that they exhibit one of 
the hazardous waste characteristics (see Sec.  261.20 through Sec.  
261.24), the waste would continue to be regulated as a hazardous waste.
---------------------------------------------------------------------------

    \18\ The ``mixture'' rule at Sec.  261.3(a)(2)(iv) provides 
that, with limited exceptions, any mixture of a listed hazardous 
waste and a solid waste is itself a hazardous waste.
---------------------------------------------------------------------------

1. How Generators Document Compliance With the Landfill Condition
    Under the proposed option number one, generators of wastewater 
treatment sludges claimed to be nonhazardous are responsible for 
ensuring that shipments of such waste are placed in landfill units that 
meet the design criteria specified in Sec.  258.40, Sec.  264.301, or 
Sec.  265.301. Under option two, generators would also need to document 
compliance if they send their waste shipments to a state-permitted 
landfill unit that has an adequate single clay liner. Under either 
option, generators wishing to qualify for the exemption from the F019 
listing would be required to maintain records to show that their wastes 
are placed in an appropriate landfill unit, whether the unit is at a 
municipal solid waste landfill, hazardous waste landfill, or an 
industrial solid waste landfill (in the case of option two, this would 
include disposal in a unit with a single clay liner). EPA is proposing 
a flexible performance standard that would allow the generator to 
demonstrate that shipments of waste were received by a landfill unit 
that is subject to or meets the landfill design standards set out in 
the listing description through various means. A generator may be able 
to demonstrate fulfillment of the landfill disposal condition by means 
of a signed contract with the owner/operator of a municipal solid waste 
landfill, a hazardous waste landfill, or an industrial solid waste 
landfill receiving the waste; the generator should also retain specific 
shipping documents to demonstrate that the contract was implemented. 
The contract must show that the landfill owner/operator would use only 
units subject to the applicable Part 258 or Part 264 or Part 265 design 
requirements (under option two, the contract, state permit, or 
documentation from the state may also be used to document that units 
meeting the single liner specifications would be used). A generator may 
also be able to support a claim of fulfilling the landfill design 
requirements by means of signed nonhazardous waste bills of lading, 
manifests, or invoices documenting delivery, provided they show that 
wastes were placed in municipal solid waste landfill units subject to 
the applicable Part 258 design requirements or Subtitle C landfill 
units subject to the Part 264 or Part 265 design requirements. 
Similarly, the generator would be responsible for documenting that non-
municipal, nonhazardous waste landfill units (industrial landfill 
units) meet the specified liner standards. States have regulations 
governing the design of such industrial solid waste landfills, and 
landfill operators must have certifications or permit conditions 
available to provide to generators who wish to use such landfills 
instead of municipal solid waste or hazardous waste landfill units. 
Therefore, state regulations could help support a claim that the 
nonhazardous waste bills of lading, manifests, or invoices documenting 
delivery satisfy the applicable liner requirements.
2. Consequences of Failing To Meet the Disposal Conditions or 
Recordkeeping Requirements
    Disposal in a landfill subject to or meeting the landfill design 
requirements is a condition of the exemption to the listing under the 
two approaches being proposed. If a generator does not fulfill this 
condition, the sludges would be F019 listed wastes, subject to the 
applicable Subtitle C requirements. Therefore, the Agency advises 
generators to properly store the wastewater treatment sludges that are 
claimed to be nonhazardous wastes to ensure that improper releases do 
not occur. EPA encourages all generators to store all wastes in 
containers, tanks, or buildings, so as to reduce potential releases to 
the environment through spills, wind dispersal, and precipitation. The 
exemption for these wastes is conditioned upon disposal in the landfill 
units that are subject to, or otherwise meet, the specified design 
criteria.
    In addition, a generator claiming that the wastewater treatment 
sludges are not F019 listed waste must maintain sufficient 
documentation to demonstrate that shipments of such waste were disposed 
in a landfill subject to or meeting the liner design standards 
specified under the conditional exemption. The proposed regulatory text 
(Sec.  261.31(b)(4)(iii)) specifies necessary records that a generator 
claiming the exemption must keep.
    Generators taking advantage of the exemption that fail to meet the 
condition of disposing the wastewater treatment sludges in a landfill 
unit that meets certain liner design criteria would be subject to 
enforcement action, and the wastewater treatment sludges may be 
considered to be hazardous waste from the point of their generation. 
EPA could choose to bring an enforcement action under RCRA Sec.  
3008(a) for all violations of hazardous waste regulatory requirements 
occurring from the time the wastewater treatment sludges are generated 
up to the time they are finally disposed. Releases of hazardous waste 
could also potentially be addressed through enforcement orders, such as 
orders under RCRA Sec. Sec.  3013 and 7003. States could choose to take 
an enforcement action for violations of state hazardous waste 
requirements under state authorities.
    Generators claiming the exemption from the F019 listing must be 
able to demonstrate to the appropriate

[[Page 2230]]

regulatory agency that the condition of the exemption is being met. In 
accordance with existing requirements, the facility claiming the 
exemption bears the burden of proof to demonstrate conformance with the 
requirements specified in the regulation. See 40 CFR 261.2(f).
    EPA requests comment on whether the proposed record-keeping 
requirements should also be made conditions of the exemption, rather 
than established as separate recordkeeping requirements. In addition, 
the Agency seeks comments on whether additional requirements or 
conditions are necessary to ensure that the waste is not improperly 
disposed or released prior to disposal in landfills meeting the 
landfill requirements in Sec.  258.40, Sec.  264.301 or Sec.  265.310 
(or under the second proposed option, a municipal or industrial solid 
waste landfill with a single clay liner). EPA is considering the need 
to include a condition for the exemption that the waste be stored so as 
to minimize releases to the environment. The regulatory condition being 
considered by the Agency could include the following possible 
regulatory language.

    Generators of wastewater treatment sludges that are claimed to 
be nonhazardous must manage such wastes in a manner that prevents 
their loss to the environment. Such wastes must be stored in tanks, 
containers, or buildings that are constructed and maintained in a 
way that prevents releases of these materials into the environment. 
At a minimum, any building used for this purpose must be an 
engineered structure that has a floor, walls and a roof to prevent 
wind dispersal and contact with precipitation. Tanks used for this 
purpose must be structurally sound and, if outdoors, must have roofs 
or covers that prevent contact with wind and precipitation. 
Containers, such as super sacks, drums, or roll-on/roll-off 
containers, used for this purpose must be kept closed except when it 
is necessary to add or remove material, and must be in sound 
condition. Generators may store the waste on site for no longer than 
90 days.

EPA may make all or some of these requirements conditions in the final 
rule.\19\
---------------------------------------------------------------------------

    \19\ For a facility that generates a volume of 3,000 cy/yr, an 
average weekly volume would be about 60 cy. This would probably 
require 2 to 3 dumpsters (20 to 40 cy in size). Given that 
generators are unlikely to want to store many dumpsters, we believe 
that a 90 day limit is reasonable and would not be burdensome.
---------------------------------------------------------------------------

    EPA obtained information from delisting petitions that indicates 
generators of the F019 sludge store the dewatered sludges in containers 
or bins prior to shipment offsite for disposal. During visits to three 
vehicle manufacturing plants generating sludges, EPA found that sludge 
dewatering equipment and sludge containers were kept inside buildings, 
reducing any potential for releases. While these management practices 
may reflect the fact that the delisted sludges were previously 
hazardous waste, we expect that these practices would continue after an 
exemption.\20\ We seek any further information from commenters as to 
the current sludge management practices at facilities that currently 
generate F019 wastes (or delisted F019), and any information on 
practices at vehicle manufacturers that do not currently generate F019 
(i.e., plants that do not use aluminum). If such information indicates 
that generators are already handling the waste to minimize releases, 
the Agency will take this into consideration when deciding whether 
storage conditions are necessary.
---------------------------------------------------------------------------

    \20\ Two facilities were generating delisted F019 sludges, and 
one had just added conversion coating of aluminum to its process and 
eventually obtained a delisting. See note to docket on site visits 
by Mr. James Michael.
---------------------------------------------------------------------------

3. Land Disposal Restrictions
    The Agency today is proposing to amend the F019 listing to exclude 
wastewater treatment sludges from zinc phosphating, when such 
phosphating is used at motor vehicle manufacturers. These wastewater 
treatment sludges will not be hazardous if the wastes are disposed in a 
landfill unit subject to, or otherwise meeting, the landfill 
requirements for the liner systems specified in the F019 listing under 
both of the proposed options.
    40 CFR Part 268 prohibits the land disposal of RCRA hazardous waste 
unless they have been treated to meet a certain level or by a 
technology specified by EPA. See Table 1.Treatment Standards for 
Hazardous Wastes in Sec.  268.40. The land disposal restrictions only 
apply to solid wastes that are RCRA hazardous wastes. Therefore, if the 
wastewater treatment sludges are disposed in landfill units that are 
subject to or meet the landfill design criteria outlined in today's 
proposal, they would not be hazardous waste from the point of 
generation and, thus, not subject to the land disposal restriction 
requirements.

B. Interrelationship Between Proposed Rule and Current F019 Delistings

    The question arises as to the status of waste generated by 
facilities that currently have an exemption for their wastes through a 
delisting under Sec.  260.22. Today's proposed revision to the F019 
listing would exempt wastes from motor vehicle manufacturing facilities 
that meet the landfill disposal conditions. Thus, wastes that are to be 
disposed in a subtitle D or subtitle C unit that meets the liner design 
standards specified in the listings are exempted from the listing from 
their point of generation. As such, the exempt waste would not be 
subject to any RCRA subtitle C management requirements for generation, 
storage, transport, treatment, or disposal (including land disposal 
restrictions). These exempt wastes would never become F019 listed 
wastes (when the specified disposal conditions are met), and, thus, the 
existing delistings (including any conditions associated with the 
delisting) would be rendered moot by today's proposal, presuming the 
authorized state adopts the rule, where applicable. However, EPA 
realizes that facilities with delistings may wish to avoid any 
confusion that might arise in the implementation of the exemption 
proposed in today's notice. Therefore, the facility may wish to seek to 
have its delisting withdrawn by the regulatory authority (the EPA 
Region or state), unless the facility wishes to continue to manage its 
waste pursuant to its existing delisting. However, EPA encourages 
facilities with delistings to be sure that the state in which they 
operate has adopted the exemption prior to moving to drop an existing 
delisting. See the discussion below in Section VII. State Authorization 
for additional information on the authorization process.

VII. State Authorization

    Under section 3006 of RCRA, EPA may authorize a qualified state to 
administer and enforce a hazardous waste program within the state in 
lieu of the federal program, and to issue and enforce permits in the 
state. Following authorization, the state requirements authorized by 
EPA apply in lieu of equivalent Federal requirements and become 
Federally-enforceable as requirements of RCRA. EPA maintains 
independent authority to bring enforcement actions under RCRA sections 
3007, 3008, 3013, and 7003. Authorized states also have independent 
authority to bring enforcement actions under state law.
    A state may receive authorization by following the approval process 
described in 40 CFR part 271. Part 271 of 40 CFR also describes the 
overall standards and requirements for authorization. After a state 
receives initial authorization, new Federal regulatory requirements 
promulgated under the authority in the RCRA statute do not apply in 
that state until the state adopts and receives authorization for 
equivalent state requirements. The state

[[Page 2231]]

must adopt such requirements to maintain authorization. In contrast, 
under RCRA section 3006(g), (42 U.S.C. 6926(g)), new Federal 
requirements and prohibitions imposed pursuant to the 1984 Hazardous 
and Solid Waste Amendments (HSWA) take effect in authorized states at 
the same time that they take effect in unauthorized states. Although 
authorized states still are required to update their hazardous waste 
programs to remain equivalent to the Federal program, EPA carries out 
HSWA requirements and prohibitions in authorized states, including the 
issuance of new permits implementing those requirements, until EPA 
authorizes the state to do so. Authorized states are required to modify 
their programs only when EPA promulgates Federal requirements that are 
more stringent or broader in scope than existing Federal requirements.
    RCRA section 3009 allows the states to impose standards more 
stringent than those in the Federal program. See also 40 CFR 271.1(i). 
Therefore, authorized states are not required to adopt Federal 
regulations, either HSWA or non-HSWA, that are considered less 
stringent.
    Today's rule is proposed pursuant to non-HSWA authority. The 
proposed changes in this rule are less stringent than the current 
Federal requirements. Therefore, states will not be required to adopt 
and seek authorization for the proposed changes. EPA will implement the 
changes to the exemptions only in those states which are not authorized 
for the RCRA program. Nevertheless, EPA believes that this proposed 
rulemaking has considerable merit, and the Agency thus strongly 
encourages states to amend their programs and become Federally-
authorized to implement these rules once they become final.

VIII. Comprehensive Environmental Response, Compensation, and Liability 
Act (CERCLA) Designation and List of Hazardous Substances and 
Reportable Quantities

    The Comprehensive Environmental Response, Compensation, and 
Liability Act of 1980 (CERCLA) defines the term ``hazardous substance'' 
to include RCRA listed and characteristic hazardous wastes. When EPA 
adds a hazardous waste under RCRA, the Agency also will add the waste 
to its list of CERCLA hazardous substances. EPA also establishes a 
reportable quantity, or RQ, for each CERCLA hazardous substance. EPA 
provides a list of the CERCLA hazardous substances along with their RQs 
in Table 302.4 at 40 CFR 302.4. If a person in charge of a vessel or 
facility that releases a CERCLA hazardous substance in an amount that 
equals or exceeds its RQ, then that person must report that release to 
the National Response Center (NRC) pursuant to CERCLA section 103. That 
person also may have to notify state and local authorities.
    Because today's rule is proposing to modify the scope of the EPA 
Hazardous Waste No. F019 under 40 CFR 261.31 listing to exclude 
wastewater treatment sludges from zinc phosphating, when such 
phosphating is used in the motor vehicle manufacturing process, and if 
the wastes are disposed in a landfill is subject to, or meets certain 
liner design requirements, the Table 302.4 at 40 CFR 302.4 would be 
modified to adopt the same definition and scope.

IX. Relationship to Other Rules--Clean Water Act

    We believe that today's proposed regulatory changes will not: (1) 
Increase the amount of discharged wastewater pollutants at the industry 
or facility levels; or (2) interfere with the ability of industrial 
generators and recyclers of electroplating residuals to comply with the 
Clean Water Act requirements (e.g., Metal Finishing Effluent 
Guidelines, 40 CFR Part 433).

X. Statutory and Executive Order Reviews

A. Executive Order 12866: Regulatory Planning and Review

    Under Executive Order 12866 (58 FR 51735), the Agency must 
determine whether this regulatory action is ``significant'' and 
therefore subject to formal review by the Office of Management and 
Budget (OMB) and to the requirements of the Executive Order, which 
include assessing the costs and benefits anticipated as a result of the 
proposed regulatory action. The Order defines ``significant regulatory 
action'' as one that is likely to result in a rule that may: (1) Have 
an annual effect on the economy of $100 million or more or adversely 
affect in a material way the economy, a sector of the economy, 
productivity, competition, jobs, the environment, public health or 
safety, or state, local, or tribal governments or communities; (2) 
create a serious inconsistency or otherwise interfere with an action 
taken or planned by another agency; (3) materially alter the budgetary 
impact of entitlements, grants, user fees, or loan programs or the 
rights and obligations of recipients thereof; or (4) raise novel legal 
or policy issues arising out of legal mandates, the President's 
priorities, or the principles set forth in the Executive Order.
    Pursuant to the terms of Executive Order 12866, although the annual 
effect of this proposed rule is expected to be less than $100 million, 
the Agency has determined that today's proposed rule is a significant 
regulatory action because this proposed rule contains novel policy 
issues. As such, this action was submitted to OMB for review. Changes 
made in response to OMB suggestions or recommendations are documented 
in the docket to today's proposal.
    The following is a summary of EPA's economic analysis as contained 
in the Economics Background Document in support of this proposal, which 
is available for public review and comment in the EPA Docket 
(http://www.regulations.gov). Although 73 industries in 42 states generate 0.7 

million tons per year of RCRA F019 hazardous waste sludge as of 1999, 
the scope of this F019 proposed rule is limited to the (1) automobile 
manufacturing industry (NAICS 336111) and (2) the light truck/utility 
vehicle manufacturing industry (NAICS 336112). The Agency defined this 
scope in relation to 15 recent (1997-2005) delisting final 
determinations for these two motor vehicle manufacturing industries in 
EPA Regions 4 and 5.\21\ Under the current F019 listing description, 
motor vehicle manufacturers become F019 sludge generators if they use 
aluminum parts on vehicle bodies which undergo the chemical conversion 
(zinc phosphating) process. Motor vehicle manufacturers began in the 
early 1970's, to substitute lighter-weight aluminum parts for heavier 
steel parts to achieve national vehicle fleet fuel efficiency and 
vehicle pollutant emission reduction objectives. If promulgated, the 
proposed elimination of RCRA Subtitle C hazardous waste regulatory 
requirements for waste transport, waste treatment/disposal, and waste 
reporting/recordkeeping in this proposed rule, is expected to provide 
$1.6 to $4.6 million per year in regulatory cost savings to 14 
facilities in these two industries which

[[Page 2232]]

are known as of 2005 to generate about 8,700 tons per year of F019 
sludge, but are not yet delisted (as of year-end 2005). Although 
today's proposed action presents alternative RCRA Subtitle D non-
hazardous waste landfill liner specifications (i.e., liner design 
criteria) as possible conditions for exemption of F019 sludge from RCRA 
Subtitle C regulation, the economic impact analysis does not 
distinguish landfill liner types in this cost savings estimate. 
Secondary impacts of the proposed rule may also include potential 
future RCRA regulatory cost avoidance for up to 39 other facilities in 
these two industries not currently generating F019 sludge, but which 
may begin applying aluminum parts in vehicle assembly. Furthermore, by 
reducing regulatory costs, EPA anticipates that this rule may also 
induce other motor vehicle manufacturing facilities to begin using 
aluminum in vehicles sooner than they otherwise would, thereby possibly 
accelerating future achievement of national air quality and fuel 
efficiency objectives. The Economics Background Document provides 
estimates for these secondary and induced benefits for this proposed 
rule.
---------------------------------------------------------------------------

    \21\ The Federal Register (FR) citations for the 15 delisting 
determinations for F019 are: GM in Lake Orion, Michigan (62 FR 
55344, October 24, 1997); GM in Lansing, Michigan (65 FR 31096, May 
16, 2000); BMWMC in Greer, South Carolina (66 FR 21877, May 2, 
2001); Nissan in Smyrna, Tennessee (67 FR 42187, June 21, 2002); GM 
in Pontiac, Michigan, GM in Hamtramck, Michigan, GM in Flint, 
Michigan, GM Grand River in Lansing, Michigan, Ford in Wixom, 
Michigan, Ford in Wayne, Michigan (68 FR 44652, July 30, 2003); 
DaimlerChrylser Jefferson North in Detroit, Michigan (69 FR 8828, 
February 26, 2004); GM in Lordstown, Ohio (69 FR 60557, October 12, 
2004); Ford in Dearborn, Michigan (70 FR 21153, April 25, 2005); GM 
in Janesville, Wisconsin (70 FR 71002, November 25, 2005); and, GM 
Saturn in Spring Hill, Tennessee (70 FR 76168, December 23, 2005).
---------------------------------------------------------------------------

B. Paperwork Reduction Act

    The information collection requirements in this proposed rule have 
been submitted for approval to the Office of Management and Budget 
(OMB) under the Paperwork Reduction Act, 44 U.S.C. 3501 et seq. An 
Information Collection Request (ICR) document prepared by EPA has been 
assigned EPA ICR number 1189.18 and a copy may be obtained from Susan 
Auby by mail at U.S. Environmental Protection Agency, Collection 
Strategies Division (Mail Code 2822), 1200 Pennsylvania Avenue, NW., 
Washington DC 20460, by e-mail at auby.susan@epa.gov, or by calling 
(202) 566-1672. A copy may also be downloaded from the Internet at 
http://www.epa.gov/icr.

    EPA under 40 CFR 261.31(b)(4)(iii), proposes to add a recordkeeping 
requirement for generators. The proposed rule will require generators 
wanting to demonstrate compliance with the provisions of this proposal 
to maintain onsite for a minimum of three years documentation 
demonstrating that each shipment of waste was received by a landfill 
unit that is subject to or meets the landfill design criteria set out 
in the listing description. An enforcement action by the Agency can 
extend the record retention period (Sec.  268.7(a)(8)) beyond the three 
years.
    EPA estimates that the total annual respondent burden for the new 
paperwork requirements in the rule is approximately 35 hours per year 
and the annual respondent cost for the new paperwork requirements in 
the rule is approximately $2,600. However, in addition to the new 
paperwork requirements in the rule, the Agency also estimated the 
burden and cost that generators could expect as a result of complying 
with the existing RCRA hazardous waste information collection 
requirements for the exempted materials (e.g., preparation of hazardous 
waste manifests, biennial reporting). Taking both the new proposed and 
existing RCRA requirements into account, EPA expects the rule would 
result in a net reduction in national annual paperwork burden to the 14 
initially affected NAICS 336111 and 336112 facilities of approximately 
920 hours and $67,300. As summarized in the Economics Background 
Document and in the prior sub-section of this notice, EPA expects this 
net cost savings to be further supplemented by annual cost savings to 
these same facilities from reduced waste management costs, by the 
expected shift of sludge management from RCRA Subtitle C hazardous 
waste management, to RCRA Subtitle D nonhazardous waste management. The 
net cost to EPA of administering the rule is expected to be negligible, 
since facilities are not required under this proposed rule to submit 
any information to the Agency for review and approval. Burden means the 
total time, effort, or financial resources expended by persons to 
generate, maintain, retain, or disclose or provide information to or 
for a Federal agency. This includes the time needed to review 
instructions; develop, acquire, install, and utilize technology and 
systems for the purposes of collecting, validating, and verifying 
information, processing and maintaining information, and disclosing and 
providing information; adjust existing systems to comply with any 
previously applicable instructions and requirements; train personnel to 
be able to respond to a collection of information; search data sources; 
complete and review the collection of information; and transmit or 
otherwise disclose the information.
    An Agency may not conduct or sponsor, and a person is not required 
to respond to, a collection of information unless it displays a 
currently valid OMB control number. The OMB control numbers for EPA's 
regulations are listed in 40 CFR Part 9.
    To comment on the Agency's need for this information, the accuracy 
of the provided burden estimates, and any suggested methods for 
minimizing respondent burden, including the use of automated collection 
techniques, EPA has established a public docket for this rule, which 
includes this ICR, under Docket ID No. EPA-HQ-RCRA-2006-0984. Submit 
any comments related to the ICR for this proposed rule to EPA and OMB. 
See ADDRESSES section at the beginning of this notice for where to 
submit comments to EPA. Send comments to OMB at the Office of 
Information and Regulatory Affairs, Office of Management and Budget, 
Attn: Desk Officer for EPA, 725 17th Street, NW., Washington, DC 20503.

C. Regulatory Flexibility Act

    The Regulatory Flexibility Act (RFA), as amended by the Small 
Business Regulatory Enforcement Fairness Act of 1996 (SBREFA), 5 U.S.C. 
601 et seq., generally requires an agency to prepare a regulatory 
flexibility analysis of any rule subject to notice and comment 
rulemaking requirements under the Administrative Procedure Act or any 
other statute, unless the agency certifies that the rule will not have 
a significant economic impact on a substantial number of small 
entities. Small entities include small businesses, small organizations, 
and small governmental jurisdictions.
    For purposes of assessing the impacts of today's rule on small 
entities potentially subject to this action, ``small entity'' is 
defined according to the for-profit small business size standards set 
by the Small Business Administration (SBA), in reference to the two 
six-digit NAICS code industries affected by this action: (1) NAICS 
336111 automobile manufacturing SBA standard of less than 1,000 
employees, and (2) NAICS 336112 light truck and utility vehicle 
manufacturing SBA standard of less than 1,000 employees. Today's action 
does not directly affect small governmental jurisdictions (i.e., a 
government of a city, county, town, school district or special district 
with a population of less than 50,000), or small organizations (i.e., 
any not-for-profit enterprise which is independently owned and operated 
and is not dominant in its field).
    According to the most recent U.S. Census Bureau ``Economics 
Census'' data for these two NAICS codes--for data year 2002 published 
in December 2004 and May 2005, respectively--there were 176 NAICS 
336111 establishments operated in 2002 by 161 companies, of which 154 
establishments (88%) had less than 1,000 employees (http://www.census.gov/prod/ec02/ec0231i336111t.pdf
), and there were 97 NAICS 

336112 establishments operated in 2002 by 69 companies, of which 62 
establishments (64%) had less than

[[Page 2233]]

1,000 employees (http://www.census.gov/prod/ec02/ec0231i336112t.pdf). 

These census statistics reveal that both industries consist of large 
fractions of small establishments according to the SBA definitions, but 
the census data do not reveal the fraction of companies which are small 
(which is the more relevant measure). However, it may be inferred that 
there are large fractions of small companies in both industries, 
because of the high degree of parity between establishment counts and 
companies counts of 0.96 for NAICS 336111 (i.e., 154:to:161), and of 
0.71 for NAICS 336112 (i.e., 69:to:97).
    Because this action is designed to lower the cost of waste 
management for these industries, this proposal will not result in an 
adverse economic impact effect on affected entities. Consequently, I 
hereby certify that this proposal will not have a significant economic 
impact on a substantial number of small entities. In determining 
whether a rule has a significant economic impact on a substantial 
number of small entities, the impact of concern is any significant 
adverse economic impact on small entities, since the primary purpose of 
the regulatory flexibility analyses is to identify and address 
regulatory alternatives ``which minimize any significant economic 
impact of the proposed rule on small entities'' (5 U.S.C. 603 and 604). 
Thus, an agency may certify that a rule will not have a significant 
economic impact on a substantial number of small entities if the rule 
relieves regulatory burden, or otherwise has a positive economic effect 
on small entities subject to the rule. For more information regarding 
the economic impact of this proposed rule, please refer to the 
``Economics Background Document'' available from the EPA Docket 
(http://www.regulations.gov).

    EPA therefore concludes that today's proposed rule will relieve 
regulatory burden for all size entities, including small entities. The 
Agency continues to be interested in the potential impacts of the 
proposed rule on small entities and welcomes comments on issues related 
to such impacts.

D. Unfunded Mandates Reform Act

    Title II of the Unfunded Mandates Reform Act of 1995 (UMRA), Public 
Law 104-4, establishes requirements for Federal Agencies to assess the 
effects of their regulatory actions on state, local, and tribal 
governments and the private sector. Under section 202 of the UMRA, EPA 
must prepare a written analysis, including a cost-benefit analysis, for 
proposed and final rules with ``Federal mandates'' that may result in 
expenditures to state, local, and tribal governments, in the aggregate, 
or to the private sector, of $100 million or more in any one year. 
Before promulgating an EPA rule for which a written statement is 
needed, section 205 of the UMRA requires EPA to identify and consider a 
reasonable number of regulatory alternatives and adopt the least 
costly, most cost-effective, or least burdensome alternative that 
achieves the objectives of the rule. The provisions of section 205 do 
not apply when they are inconsistent with applicable law. Moreover, 
section 205 allows EPA to adopt an alternative other than the least 
costly, most cost-effective or least burdensome alternative if the 
Administrator publishes with the final rule an explanation why that 
alternative was not adopted.
    Before EPA establishes any regulatory requirements that may 
significantly or uniquely affect small governments, including tribal 
governments, it must have developed under section 203 of the UMRA a 
small government agency plan. The plan must provide for notifying 
potentially affected small governments, enabling officials to have 
meaningful and timely input in the development of regulatory proposals, 
and informing, educating, and advising small governments on compliance 
with the regulatory requirements.
    EPA has determined that this rule does not include a Federal 
mandate that may result in expenditures of $100 million or more for 
state, local, or tribal governments, in the aggregate, or the private 
sector in any one year. This is because this proposed rule imposes no 
enforceable duty on any state, local, or tribal governments. EPA also 
has determined that this rule contains no regulatory requirements that 
might significantly or uniquely affect small governments. In addition, 
as discussed above, the private sector is not expected to incur costs 
exceeding $100 million. Therefore, today's proposed rule is not subject 
to the requirements of sections 202 and 205 of UMRA.

E. Executive Order 13132: Federalism

    Executive Order 13132, entitled ``Federalism'' (64 FR 43255, August 
10, 1999), requires EPA to develop an accountable process to ensure 
``meaningful and timely input by state and local officials in the 
development of regulatory policies that have federalism implications.'' 
``Policies that have federalism implications'' is defined in the 
Executive Order to include regulations that have ``substantial direct 
effects on the states, on the relationship between the national 
government and the states, or on the distribution of power and 
responsibilities among the various levels of government.''
    This proposal does not have federalism implications. It will not 
have substantial direct effects on the states, on the relationship 
between the national government and the states, or on the distribution 
of power and responsibilities among the various levels of government, 
as specified in Executive Order 13132. This rule directly affects 
primarily generators of hazardous waste sludges in the NAICS 3361 motor 
vehicle manufacturing industry group. There are no state and local 
government bodies that incur direct compliance costs by this 
rulemaking. State and local government implementation expenditures are 
expected to be less than $500,000 in any one year. Thus, the 
requirements of Section 6 of the Executive Order do not apply to this 
proposal.
    In the spirit of Executive Order 13132, and consistent with EPA 
policy to promote communications between EPA and state and local 
governments, EPA specifically solicits comment on this proposed rule 
from state and local officials.

F. Executive Order 13175: Consultation and Coordination With Indian 
Tribal Governments

    Executive Order 13175, entitled ``Consultation and Coordination 
with Indian Tribal Governments'' (65 FR 67249, November 9, 2000), 
requires EPA to develop an accountable process to ensure ``meaningful 
and timely input by tribal officials in the development of regulatory 
policies that have tribal implications.'' This proposed rule does not 
have tribal implications, as specified in Executive Order 13175. 
Today's rule does not significantly or uniquely affect the communities 
of Indian tribal governments, nor would it impose substantial direct 
compliance costs on them. Thus, Executive Order 13175 does not apply to 
this rule.

G. Executive Order 13045: Protection of Children From Environmental 
Risks and Safety Risks

    The Executive Order 13045, entitled ``Protection of Children from 
Environmental Health Risks and Safety Risks'' (62 FR 19885, April 23, 
1997) applies to any rule that EPA determines (1) is ``economically 
significant'' as defined under Executive Order 12866, and (2) the 
environmental health or safety risk addressed by the rule has a 
disproportionate effect on children. If the regulatory action meets 
both criteria, the Agency must evaluate the environmental health or 
safety effects of the planned rule on children; and

[[Page 2234]]

explain why the planned regulation is preferable to other potentially 
effective and reasonably feasible alternatives considered by the 
Agency.
    This proposal is not subject to the Executive Order because it is 
not economically significant as defined in Executive Order 12866, and 
because the Agency does not have reason to believe the environmental 
health or safety risks addressed by this proposed rule present a 
disproportionate risk to children.

H. Executive Order 13211: Actions that Significantly Affect Energy 
Supply, Distribution or Use

    This proposed rule is not a ``significant energy action'' as 
defined in Executive Order 13211, ``Actions Concerning Regulations That 
Significantly Affect Energy Supply, Distribution, or Use'' (66 FR 28355 
(May 22, 2001)) because it is not likely to have a significant adverse 
effect on the supply, distribution, or use of energy. This proposed 
rule reduces regulatory burden and as explained in our ``Economics 
Background Document,'' and may possibly induce fuel efficiency and 
energy savings in the national motor vehicle fleet. It thus should not 
adversely affect energy supply, distribution or use.

I. National Technology Transfer and Advancement Act

    Section 12(d) of the National Technology Transfer and Advancement 
Act of 1995 (``NTTAA''), Public Law 104-113, section 12(d) (15 U.S.C. 
272 note) directs EPA to use voluntary consensus standards in its 
regulatory activities, unless to do so would be inconsistent with 
applicable law or otherwise impractical. Voluntary consensus standards 
are technical standards (e.g., materials specifications, test methods, 
sampling procedures, and business practices) that are developed or 
adopted by voluntary consensus standards bodies. The NTTAA directs EPA 
to provide Congress, through OMB, explanations when the Agency decides 
not to use available and applicable voluntary consensus standards. This 
proposed rulemaking does not involve technical standards. Therefore, 
EPA is not considering the use of any voluntary consensus standards.

J. Executive Order 12898: Federal Actions To Address Environmental 
Justice in Minority Populations and Low-Income Populations

    Executive Order 12898, ``Federal Actions to Address Environmental 
Justice in Minority Populations and Low-Income Population'' (February 
11, 1994), is designed to address the environmental and human health 
conditions of minority and low-income populations. EPA is committed to 
addressing environmental justice concerns and has assumed a leadership 
role in environmental justice initiatives to enhance environmental 
quality for all citizens of the United States. The Agency's goals are 
to ensure that no segment of the population, regardless of race, color, 
national origin, income, or net worth bears disproportionately high and 
adverse human health and environmental impacts as a result of EPA's 
policies, programs, and activities. Our goal is to ensure that all 
citizens live in clean and sustainable communities. In response to 
Executive Order 12898, and to concerns voiced by many groups outside 
the Agency, EPA's Office of Solid Waste and Emergency Response (OSWER) 
formed an Environmental Justice Task Force to analyze the array of 
environmental justice issues specific to waste programs and to develop 
an overall strategy to identify and address these issues (OSWER 
Directive No. 9200.3-17).
    The Agency's risk assessment did not identify risks from the 
management of the zinc phosphating sludge generated by the motor 
vehicle manufacturing industry provided that the waste is disposed in a 
landfill that is subject to or meets the landfill design criteria set 
out in today's proposal. Therefore, EPA believes that any populations 
in proximity to the landfills used by these facilities should not be 
adversely affected by common waste management practices for the 
wastewater treatment sludge.

List of Subjects

40 CFR Part 261

    Environmental protection, Hazardous materials, Recycling, Waste 
treatment and disposal.

40 CFR Part 302

    Environmental protection, Air pollution control, Chemicals, 
Emergency Planning and Community Right-to-Know Act, Extremely hazardous 
substances, Hazardous chemicals, Hazardous materials, Hazardous 
materials transportation, Hazardous substances, Hazardous wastes, 
Intergovernmental relations, Natural resources, Reporting and 
recordkeeping requirements, Superfund, Waste treatment and disposal, 
Water pollution control, Water supply.

    Dated: January 11, 2007.
Stephen l. Johnson,
Administrator.
    For the reasons set out in the preamble, title 40, chapter I of the 
Code of Federal Regulations is proposed to be amended as follows:

PART 261--IDENTIFICATION AND LISTING OF HAZARDOUS WASTE

    1. The authority citation for part 261 continues to read as 
follows:

    Authority: 42 U.S.C. 6905, 6912(a), 6921, 6922, 6924(y), and 
6938.

    2. Section 261.31 is amended by:
    a. In the table in paragraph (a) by revising the alphanumeric entry 
F019.
    b. Amending paragraph (b) by adding paragraph (b)(4).
    The revisions and additions read as follows:


Sec.  261.31  Hazardous wastes from specific sources.

    (a) * * *

------------------------------------------------------------------------
   Industry and EPA hazardous
           waste No.                  Hazardous waste       Hazard code
------------------------------------------------------------------------

                              * * * * * * *
F019...........................  Wastewater treatment
                                  sludges from the
                                  chemical conversion
                                  coating of aluminum
                                  except from zirconium
                                  phosphating in aluminum
                                  can washing when such
                                  phosphating is an
                                  exclusive conversion
                                  coating process.
                                  Wastewater treatment
                                  sludges from the
                                  manufacturing of motor
                                  vehicles using a zinc
                                  phosphating process
                                  will not be hazardous
                                  if the wastes are
                                  disposed in a landfill
                                  unit subject to, or
                                  otherwise meeting, the
                                  landfill requirements
                                  in Sec.   258.40, Sec.
                                   264.301 or Sec.
                                  265.301. For the
                                  purposes of this
                                  listing, motor vehicle
                                  manufacturing is
                                  defined in paragraph
                                  Sec.   261.31(b)(4)(i)
                                  of this section;
                                  paragraphs Sec.
                                  261.31(b)(4)(ii) and
                                  (iii) of this section
                                  describe the
                                  responsibilities and
                                  recordkeeping
                                  requirements for motor
                                  vehicle manufacturing
                                  facilities.
                              * * * * * * *
------------------------------------------------------------------------


[[Page 2235]]

* * * * *
    (b) * * *
    (4) For the purposes of the F019 listing, the following apply to 
wastewater treatment sludges from the manufacturing of motor vehicles 
using a zinc phosphating process.
    (i) Motor vehicle manufacturing is defined to include the 
manufacture of automobiles and light trucks/utility vehicles (including 
light duty vans, pick-up trucks, minivans, and sport utility vehicles). 
Facilities must be engaged in manufacturing complete vehicles (body and 
chassis or unibody) or chassis only.
    (ii) Generators of wastewater treatment sludges that are claimed to 
be nonhazardous must ensure that shipments of such waste are placed in 
landfill units that are subject to or meet the landfill design criteria 
specified in the F019 listing description.
    (iii) Generators must maintain in their on-site records 
documentation and information sufficient to prove that the wastewater 
treatment sludges to be exempted from the F019 listing meet the 
condition of the listing. These records must include the volume of 
waste generated and disposed of off-site. Generators must maintain 
these documents on site for no less than three years. The retention 
period for the documentation is automatically extended during the 
course of any enforcement action or as requested by the Regional 
Administrator or the state regulatory authority.

PART 302--DESIGNATION, REPORTABLE QUANTITIES, AND NOTIFICATION

    3. The authority citation for part 302 continues to read as 
follows:

    Authority: 42 U.S.C. 9602, 9603, and 9604; 33 U.S.C. 1321 and 
1361.

    4. In Sec.  302.4, Table 302.4 is amended by revising the entry for 
F019 in the table to read as follows:


Sec.  302.4  Designation of hazardous substances.

* * * * *

                      TABLE 302.4.--List Of Hazardous Substances and Reportable Quantities
                         [Note: All comments/notes are located at the end of this table]
----------------------------------------------------------------------------------------------------------------
                                                        Statutory code                          Final RQ pounds
      Hazardous substance               CASRN              [cross5]         RCRA Waste No.           (Kg)
----------------------------------------------------------------------------------------------------------------

                                                  * * * * * * *
F019...........................  ...................  ..................  4 F019............  10 (4.54)
Wastewater treatment sludges
 from the chemical conversion
 coating of aluminum except
 from zirconium phosphating in
 aluminum can washing when such
 phosphating is an exclusive
 conversion coating process.
 Wastewater treatment sludges
 from the manufacturing of
 motor vehicles using a zinc
 phosphating process will not
 be hazardous if the wastes are
 disposed in a landfill unit
 subject to, or otherwise
 meeting, the landfill
 requirements in Sec.   258.40,
 Sec.   264.301 or Sec.
 265.301. For the purposes of
 this listing, motor vehicle
 manufacturing is defined in
 paragraph Sec.
 261.31(b)(4)(i) of this
 section; paragraphs Sec.
 261.31(b)(4)(ii) and (iii) of
 this section describe the
 responsibilities and
 recordkeeping requirements for
 motor vehicle manufacturing
 facilities.
----------------------------------------------------------------------------------------------------------------

* * * * *
[FR Doc. E7-640 Filed 1-17-07; 8:45 am]

BILLING CODE 6560-50-P
