National Emission Standards for Hazardous Air Pollutants; Proposed Standards for Hazardous Air Pollutant Emissions From the Printing and Publishing Industry

Federal RegisterMar 14, 1995

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ENVIRONMENTAL PROTECTION AGENCY

40 CFR Part 63

[AD-FRL-5168-8]

RIN 2060-AD95

National Emission Standards for Hazardous Air Pollutants;

Proposed Standards for Hazardous Air Pollutant Emissions From the

Printing and Publishing Industry

AGENCY: Environmental Protection Agency (EPA).

ACTION: Proposed rule and notice of public hearing.

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SUMMARY: The proposed standards would reduce emissions of hazardous air

pollutants (HAP) from existing and new printing operations that are

major sources of HAP emissions. A major source is defined in section

112(a) of the Clean Air Act as amended in 1990 (Act) as a source that

emits, or has the potential to emit, considering controls, 10 tons per

year (tpy) or more of any individual HAP or 25 tpy or more of any

combination of HAP. Some of these pollutants are emitted from

publication rotogravure and product and packaging rotogravure and wide-

web flexographic printing. These operations are covered in the proposed

rule. In these printing operations, a variety of HAP are used as

solvents and components in inks and other materials applied by

printers. The HAP emitted by the facilities covered by this proposed

rule include toluene, xylene, ethylbenzene, methanol, methyl ethyl

ketone, methyl isobutyl ketone, ethylene glycol and glycol ethers. All

of these pollutants can cause reversible or irreversible toxic effects

following exposure. The potential toxic effects include eye, nose,

throat and skin irritation; and blood cell, heart, liver and kidney

damage. The proposed rule is estimated to reduce emissions of HAP by

6,700 Mg per year. The emissions reductions achieved by these standards

when combined with the emissions reductions achieved by similar

standards, will achieve the primary goal of the Clean Air Act, which is

to ``enhance the quality of the Nation's air resources so as to promote

the public health and welfare and the productive capacity of its

population.''

The proposed rule implements section 112(d) of the Clean Air Act

Amendments of 1990 (1990 Amendments), which requires the Administrator

to regulate emissions of HAP listed in section 112(d) of the 1990

Amendments. The intent of this rule is to protect the public health by

requiring the maximum degree of reduction in emissions of HAP from new

and existing major sources, taking into consideration the cost of

achieving such emission reduction, any nonair quality, health and

environmental impacts, and energy requirements.

DATES: Comments. Comments must be received on or before May 30, 1995.

Public Hearing. Anyone requesting a public hearing must contact the

EPA no later than April 13, 1995. If a hearing is held, it will take

place on April 28, 1995, beginning at 10 a.m.

ADDRESSES: Comments. Comments should be submitted (in duplicate, if

possible) to: Air and Radiation Docket (Mail Code 6102), Attention:

Docket No. A-92-42, U. S. Environmental Protection Agency, 401 M

Street, SW, Washington, DC 20460. The EPA requests that a separate copy

also be sent to the contact person listed below.

The docket is located at the above address in room M-1500,

Waterside Mall (ground floor), and may be inspected from 8 a.m. to 5:30

p.m., Monday through Friday; telephone number (202) 260-7548, FAX (202)

260-4400. A reasonable fee may be charged for copying docket materials.

Public Hearing. If anyone contacts the EPA requesting a public

hearing by the required date (see DATES), the hearing will be held at

the EPA Office of Administration Auditorium in Research Triangle Park,

North Carolina. Persons interested in speaking at a public hearing

should contact Ms. Kim Teal, Coatings and Consumer Products Group, (MD-

13), U. S. Environmental Protection Agency, Research Triangle Park,

North Carolina 27711, telephone number (919) 541-5580. Persons

interested in attending the hearing should contact Ms. Kim Teal to

verify that it will be held.

Additional Information. For information on accessing the U.S. EPA

Technology Transfer Network electronic bulletin board and obtaining

copies of the Proposed Regulatory Text, Background Information Document

or Economic Impact Analysis, please refer to the SUPPLEMENTARY

INFORMATION section below.

FOR FURTHER INFORMATION CONTACT: For information concerning the

proposed regulation, contact Mr. David Salman at (919) 541-0859,

Coatings and Consumer Products Group, Emission Standards Division (MD-

13), U. S. Environmental Protection Agency, Research Triangle Park,

North Carolina 27711.

SUPPLEMENTARY INFORMATION: Technology Transfer Network. The Technology

Transfer Network (TTN) is one of EPA's electronic bulletin boards. The

TTN provides information and technology exchange in various areas of

air pollution control. The service is free [[Page 13665]] except for

the cost of a phone call. Dial (919) 541-5472 for up to a 14,000 bps

modem. If more information on TTN is needed call the HELP line at (919)

541-5384.

Proposed Regulatory Text. The proposed regulatory text is not

included in this Federal Register notice, but is available in Docket

No. A-92-42, or by written or telephone request from the Air and

Radiation Docket. This notice and the proposed regulatory language are

also available for downloading TTN under Clean Air Act, Recently Signed

Rules.

Background Information Document. The Background Information

Document (BID) for the proposed standards may be obtained from the

docket; the U. S. EPA Library (MD-35), Research Triangle Park, North

Carolina 27711, telephone number (919) 541-2777; or the National

Technical Information Service (NTIS), 5285 Port Royal Road,

Springfield, Virginia 22161, telephone (703) 487-4650. Please refer to

``National Emission Standards for Hazardous Air Pollutants: Printing

and Publishing Industry--Background Information for Proposed

Standards'' (EPA-453/R-95-002a). The BID is also available for

downloading on the TTN.

Economic Impact Analysis. The Economic Impact Analysis (EIA) for

the proposed standards may be obtained from the docket, the U. S. EPA

Library, or the NTIS. Please refer to ``Economic Impact Analysis for

the Printing and Publishing NESHAP'' (EPA-452/D-95-001). The EIA is

also available for downloading on the TTN.

Preamble Outline. The information presented in this preamble is

organized as follows:

I. Background

A. Regulatory Background and Purpose

B. Common Sense Initiative

II. Summary of the Proposed Rule

A. Applicability

B. Proposed Standards for Affected Sources

C. Compliance Dates

D. Compliance Extensions

E. Compliance Testing and Monitoring

F. Reporting and Recordkeeping Requirements.

III. Summary of Environmental, Energy, and Economic Impacts of the

Proposed Rule

A. Emission Reductions

B. Secondary Environmental Impacts

C. Energy Impacts

D. Cost Impacts

E. Economic Impacts

IV. Process Descriptions and Control Technologies

A. Process Descriptions

B. Control Techniques

V. Rationale for the Proposed Rule

A. Regulatory Development Process for NESHAP

B. Determining Maximum Achievable Control Technology (MACT)

``Floors''

C. Selection of Pollutant and Source Category(ies)

D. Selection of Emission Points Covered by the Proposed Rule

E. Selection of the Basis for the Proposed Rule

F. Selection of the Format of the Proposed Rule

G. Selection of Emission Test Methods and Monitoring Requirements

H. Selection of Recordkeeping and Reporting Requirements

I. Selection of Compliance Deadlines

J. Operating Permit Program

K. Pollution Prevention Considerations

L. Solicitation of Comments

VI. Administrative Requirements

A. Public Hearing

B. Docket

C. Executive Order 12866

D. Enhancing the Intergovernmental Partnership Under Executive Order

12875

E. Paperwork Reduction Act

F. Regulatory Flexibility Act

G. Clean Air Act Section 117

H. Regulatory Review

VII. Statutory Authority

I. Background.

The proposed rule addresses facilities which apply ink and other

materials to any substrate, except fabric, using rotogravure or wide-

web flexographic methods. These facilities print products such as

magazines, newspapers, supplements, packaging and wallpaper on

substrates such as paper, plastic, metal foil, and vinyl.

A. Regulatory Background and Purpose.

The Act requires, under section 112, that EPA evaluate and control

emissions of HAP. The control of HAP is to be achieved through

promulgation of emission standards under sections 112(d) and (f), and

of work practice standards under section 112(h) where appropriate, for

categories of sources that emit HAP. Pursuant to section 112(c) of the

Act, EPA published in the Federal Register the initial list of source

categories that emit HAP on July 16, 1992 (57 FR 31576). This list

includes major and area sources of HAP for which the EPA intends to

issue regulations between November 1992 and November 2000.

The Act was created, in part, ``to protect and enhance the quality

of the Nation's air resources so as to promote the public health and

welfare and the productive capacity of its population'' (the Act,

section 101(b)(1)). As such, this proposed regulation would protect the

public health by reducing emissions of HAP from publication rotogravure

and product and packaging rotogravure and wide-web flexographic

printing.

The HAP listed in section 112(b)(1) emitted by printing facilities

that would be covered by this proposed rule include toluene, xylene,

ethylbenzene, methanol, methyl ethyl ketone, methyl isobutyl ketone,

ethylene glycol and glycol ethers. All of these pollutants can cause

reversible or irreversible toxic effects following exposure. The

potential toxic effects include eye, nose, throat and skin irritation;

and blood cell, heart, liver and kidney damage. These adverse health

effects are associated with a wide range of ambient concentrations and

exposure times and are influenced by source-specific characteristics

such as emission rates and local meteorological conditions. Health

impacts are also dependent on multiple factors that affect human

variability such as genetics, age, health status (e.g., the presence of

pre-existing disease) and lifestyle.

The proposed standards will reduce HAP emissions from publication

rotogravure printing facilities by 4,750 Mg/yr (5,220 tpy) from a

baseline level of 17,500 Mg/yr (19,200 tpy). The proposed standards

will reduce HAP emissions from product and packaging rotogravure and

wide web flexographic printing facilities by 1,940 Mg/yr (2,140 tpy)

from a baseline level of 4,200 Mg/yr (4,620 tpy).

There are no significant economic impacts associated with the

proposed standards. There are no firms or facilities at risk of closure

as a result of the proposed standards and there will not be a

significant economic impact on a substantial number of small entities.

B. Common Sense Initiative

On October 17, 1994, the Administrator established the Common Sense

Initiative (CSI) Council in accordance with the Federal Advisory

Committee Act (U.S.C. App. 2, Section 9(c)) requirements. The CSI

addresses six industrial sectors. The Printing and Publishing industry

is one of these sectors.

The following are the six elements of the CSI program, as stated in

the ``Advisory Committee Charter.''

1. Regulation. Review existing regulations for opportunities to get

better environmental results at less cost. Improve new rules through

increased coordination.

2. Pollution Prevention. Actively promote pollution prevention as

the standard business practice and a central ethic of environmental

protection.

3. Recordkeeping and Reporting. Make it easier to provide, use, and

[[Page 13666]] publicly disseminate relevant pollution and

environmental information.

4. Compliance and Enforcement. Find innovative ways to assist

companies that seek to comply and exceed legal requirements while

consistently enforcing the law for those that do not achieve

compliance.

5. Permitting. Improve permitting so that it works more

efficiently, encourages innovation, and creates more opportunities for

public participation.

6. Environmental Technology. Give industry the incentives and

flexibility to develop innovative technologies that meet and exceed

environmental standards while cutting costs.

The Agency intends to work with the Printing CSI sector team and

consider its consensus recommendations concerning the proposed

standards. Even though the data collection and analysis efforts for the

proposed standards were completed before the CSI program was announced,

many aspects of the CSI are reflected in the proposed standards.

The alternatives considered in the development of this regulation,

including those alternatives selected as standards for new and existing

printing facilities are based on process and emissions data received

from over 600 printing facilities. The EPA met with industry and trade

groups on numerous occasions to discuss these data. In addition,

facilities and State regulatory authorities had the opportunity to

comment on draft versions of the proposed regulation and to provide

additional information. Two trade organizations provided extensive

comments; these comments were considered, and in some cases, today's

proposed standards reflect these comments. Of major concern to industry

were the opportunity to comply through pollution prevention by using

low HAP content materials.

The regulation allows sources flexibility to select from various

options for compliance. Sources may reduce HAP usage and emissions

through conversions to waterborne, lower HAP solvent-borne or

ultraviolet/electron beam cure materials. Alternatively, sources may

install or upgrade existing capture and control devices to meet the

proposed standard. Finally sources have the option to comply by a

combination of lower HAP materials and capture and control. Facilities

may select the most cost-effective option based on facility specific

considerations.

The proposed standards give existing facilities 3 years from the

date of promulgation to comply. This is the maximum amount of time

allowed under the Clean Air Act. This timeframe will provide the

greatest opportunity for developing and adopting low HAP content

materials, and provide sufficient time for facilities that choose to

install or upgrade capture and control equipment.

Included in the proposed rule are methods for determining initial

compliance as well as monitoring, recordkeeping, and reporting

requirements. All of these components are necessary to ensure that

sources will comply with the standards both initially and over time.

However, the EPA has made every effort to simplify the requirements in

the rule. The Agency has also attempted to maintain consistency with

existing regulations, or referencing the applicable sections, depending

on which method would be least confusing for a given situation.

Representatives from other interested EPA offices and programs, as

well as representatives from State regulatory agencies are included in

the regulatory development process as members of the Work Group. The

Work Group must review and concur with the regulation before proposal

and promulgation. Therefore, the EPA believes that the implications to

other EPA offices and programs have been adequately considered during

the development of these standards.

II. Summary of the Proposed Rule

Table 1 provides an overview of the proposed rule, including

applicability; the standards for each affected source; test methods and

procedures; and monitoring, recordkeeping, and reporting requirements.

Table 1.--Summary of Subpart KK of 40 CFR Part 63--National Emission Standards for the Printing and Publishing

Industry

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Affected source and requirement Description

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Printing and Publishing Industry:

Applicability....................... This rule applies to facilities engaged in rotogravure and wide-web

flexographic printing that are major sources as defined in 40 CFR

part 63. (63.821).

Estimated Number of Facilities...... Approximately 200 facilities are expected to be affected by the rule.

Applicable SIC codes include 2295, 2392, 2647, 2649, 2651, 2671,

2673, 2674, 2711, 2721, 2754, 2759, 3497, and 3996.

Permit Requirements................. Major sources are required to obtain operating permits in State where

facility is located according to 40 CFR part 70 and applicable State

regulations. (63.821(d)).

All Affected Sources:

Standards........................... Comply with Secs. 63.4 through 63.6 of the General Provisions of 40

CFR part 63, subpart A, except for Sec. 63.6(h). (63.823).

Compliance Dates.................... Within three years of the effective date for existing sources and upon

startup for new sources. (63.826).

Test Methods and Procedures......... See individual affected sources.

Monitoring Requirements............. See individual affected sources.

Recordkeeping Requirements.......... Comply with Sec. 63.10(b) and (c) of the General Provisions. (63.829).

Reporting Requirements.............. Initial notification, notification of performance tests, notification

of compliance status, performance test reports, startup, shutdown and

malfunction reports, summary reports, and HAP use reports as

described in Secs. 63.9-63.10. (63.830).

Publication Rotogravure Facilities:

Standards........................... Control of 92 percent of organic HAP or equivalent. (Organic HAP

emissions limited to no greater than 8 percent of the mass of

volatile matter, including water, used on a plantwide basis.)

(63.824(b)).

Performance Test Period and Tests... 1. Test Period. Each and every month. (63.824(b)).

2. Performance Test. Initial performance test for all control devices

to demonstrate compliance with overall control efficiency

requirement. (63.824(b))

[[Page 13667]]

Test Methods and Procedures......... 1. Organic HAP content determination. (63.827(b)(1)).

2. Volatile matter content determination. (63.827(c)(1)).

3. Overall control efficiency using liquid-liquid mass balance for

solvent recovery systems. (63.824(b)(1)(i).

4. Overall control efficiency determination using capture efficiency

test with continuous emission monitors. (63.824(b)(1)(ii) and

63.824(b)(2)(ii)).

5. Overall control efficiency determination using capture efficiency

test and incinerator destruction efficiency test. (63.824(b)(2)(i).

Monitoring Requirements............. 1. Hourly recording of flow rate from press to control device.

(63.828(a)(1).

2. Quarterly audit of continuous emission monitors. (63.828(a)(2)(i)).

3. Monitoring of capture system operating parameter. (63.828(a)(5)).

Product and Packaging Rotogravure

Presses and Wide-web Flexographic

Presses, or Groups of Presses

Controlled by a Common Solvent Recovery

System:

Standards........................... Control of 95 percent of organic HAP, or organic HAP emissions limited

to no greater than 0.20 kg HAP per kg of solids applied, for each

press, or group of presses controlled by a common solvent recovery

system, or organic HAP emissions limited to no greater than 0.04 kg

HAP per kg inks and other materials applied, for each press.

(63.825(b)).

Performance Test Period and Tests... 1. Test Period.

Uncontrolled Presses. Each and every month.

Presses controlled with solvent recovery systems. Each and every

month.

Presses controlled with incinerators monitoring operating parameters.

Every three hour period.

Presses controlled with incinerators using continuous emissions

monitors. Each and every month. (63.825(b) and (c)).

2. Performance Test. Initial performance test for all control devices

to demonstrate compliance with organic HAP emission rate. (63.825(g)

and (h)).

Test Methods and Procedures......... 1. Organic HAP content determination. (63.827(b)(2)).

2. Volatile matter and solids content determination. (63.827(c)(2)).

3. Overall control efficiency using liquid-liquid mass balance for

solvent recovery systems. (63.825(g).

4. Overall control efficiency determination using capture efficiency

test with continuous emission monitors. (63.825(g)(2) and

63.825(h)(2)).

5. Overall control efficiency determination using capture efficiency

test and incinerator destruction efficiency test. (63.825(h)).

Monitoring Requirements............. 1. Hourly recording of flow rate from press to control device.

(63.828(a)(1)).

2. Quarterly audit of continuous emission monitors. (63.828(a)(2)(i)).

3. Quarterly calibration of incinerator monitoring thermocouple(s).

(63.828(2)(ii)).

4. Operation of continuous emission monitors. (63.828(a)(3)).

5. Measurement of incinerator operating parameters. (63.828(a)(4)).

6. Monitoring of capture system operating parameter. (63.828(a)(5)).

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A. Applicability

The proposed rule would apply to each new and existing publication

rotogravure or product and packaging rotogravure and wide web

flexographic printing facility that is a major source, as defined under

section 112(a) of the Act. A major source is one that emits or has the

potential to emit, considering controls, 9.1 Mg/yr (10 tons/yr) or more

of any one HAP or 22.7 Mg/yr (25 tons/yr) of any combination of HAP for

all activities conducted at the facility. Publication rotogravure and

product and packaging rotogravure and wide web flexographic printing

operations at any major source that conducts other work would be

subject to the proposed standards, regardless of the relative

proportion of printing and non-printing work at the facility. Research

or laboratory facilities are not subject to the provisions of the

standards unless they are collocated with production lines.

The proposed rule uses the definition of research and laboratory

facilities from section 112(c)(7) of the Act. This section provides

that ``research or laboratory facility'' means any stationary source

whose primary purpose is to conduct research and development into new

processes and products, where such source is operated under the close

supervision of technically trained personnel and is not engaged in the

manufacture of products for commercial sale in commerce, except in a de

minimis manner.

Research activities include those activities that are employed to

develop a new rotogravure or flexographic ink, coating or other

material; a new substrate or end product; and may also include

activities devoted to optimizing the manufacture of the product. Once a

facility determines that the manufacture of this product is viable, the

EPA believes that additional activities are likely to be beyond the

research phase.

As noted in Sec. 63.821(a)(1), the proposed printing and publishing

rule would apply to facilities that are major sources as defined in 40

CFR 63.2. An important consideration in the definition of ``major

source'' is a given plant site's ``potential to emit.'' The ``potential

to emit'' is defined in 40 CFR 63.2 as follows: `` `Potential to emit'

means the maximum capacity of a stationary source to emit a pollutant

under its physical and operational design. Any physical or operational

limitation on the capacity of the stationary source to emit a

pollutant, including air pollution control equipment and restrictions

on hours of operation or on the type or amount of material combusted,

stored, or processed, shall be treated as part of its design if the

limitation or the effect it [[Page 13668]] would have on emissions is

Federally enforceable.''

A key aspect of the potential to emit definition is that

restrictions must be Federally enforceable. Examples of restrictions

that would be considered Federally enforceable are listed in a

definition in 40 CFR 63.2.

The EPA believes that there are printing and publishing facilities

whose actual emissions of HAP are substantially less than ``major''

amounts (i.e., more than 10 tons per year of any single HAP, or more

than 25 tons per year from the sum of all HAP emitted). Many of these

facilities, however, would be considered ``major sources'' that are

subject to the proposed rule because there is no Federally enforceable

restriction in place that limits their potential to emit HAP. The EPA

believes that the this rule should provide a mechanism for such

facilities to accept and document such restrictions.

The EPA proposes, in Sec. 63.821(a)(2) through (3) of the proposed

rule, that if owners or operators commit to using no more than 9.1 Mg

(10 tons) per 12 month period of each HAP and less than 22.7 Mg (25

tons) per 12 month period of any combination of HAP at the entire

facility, including materials used for source categories or purposes

other than printing and publishing, then the facility can be considered

an area source. Each facility for which the owner or operator commits

to the criteria stated in Sec. 63.821(a)(2) would be subject only to

the recordkeeping provisions in Sec. 63.829(d) and the reporting

provisions in Sec. 63.830(d) of this subpart as long as the commitment

is met for each 12 month period. If the commitment is not met for any

12 month period then the facility would be in violation of its

commitment and would be considered a major source of HAP beginning the

first month after the end of the first 12 month period in which either

of the HAP use thresholds was exceeded. As a major source of HAP, each

such facility would be subject to the provisions of this subpart as

noted in Sec. 63.821(a)(1) and would no longer be eligible to use the

provisions of Sec. 63.821(a)(2).

The EPA believes that there are sources using more than 10 tons of

an individual HAP or more than 25 tons of total HAP per 12 month period

that may emit less than ``major'' amounts (e.g., sources using capture

and control equipment that reduces HAP emissions), and for which the

owner or operator may be willing to accept case-by-case operating

restrictions that would ensure that the potential to emit does not

exceed the major source threshold. The EPA is considering adding

language to the final rule that would provide a mechanism for such

sources. The EPA requests comment on: (1) Whether such language should

be added; (2) the type of reporting and process required to establish

the case-by-case commitment (in particular, how to establish throughput

and content limitations and performance criteria for the capture and

control equipment that would ensure area source status); and (3) the

types of records that should be maintained to document compliance with

the restrictions. In addition, the EPA requests comment on whether the

level of recordkeeping and reporting should vary, depending on the

level of emissions (as reflected by the throughput and content of the

materials used, and performance of the capture and control equipment).

In general, rotogravure and wide web flexographic printing

facilities are covered by the SIC codes listed in Table 2. However,

facilities classified under other SIC codes may be subject to the

proposed standards if the facility meets the definition of a major

source and conducts rotogravure or wide web flexographic printing.

Table 2.--Rotogravure and Wide Web Flexographic Printing SIC Codes

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SIC

Code Description

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2295.. Vinyl Coated or Laminated Fabric.

2392.. House Furnishings, including Shower Curtains.

2647.. Sanitary Paper Products.

2649.. Wallcoverings.

2651.. Folding Paperboard Boxes.

2671.. Coated and Laminated Paper and Plastic Film for Packaging.

2673.. Plastic Bags and Liners, Coated and Laminated.

2674.. Uncoated Paper Bags and Sacks and Multiwall Shipping Sacks and

Bags.

2711.. Newspapers.

2721.. Periodicals.

2754.. Commercial Printing, Gravure.

2759.. Commercial Printing, NEC.

3497.. Laminated Aluminum Foil, Flexible Packaging.

3996.. Hard Surface Floor Coverings.

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Based on information obtained through an information collection

request and information provided by the Gravure Association of America

(GAA), there are an estimated 200 facilities that will be subject to

the proposed standards. The combined HAP emissions from these

facilities are estimated to be over 21,800 Mg/yr (24,000 tpy).

Affected Sources

The proposed rule would limit organic HAP emissions that result

from publication rotogravure and product and packaging rotogravure and

wide-web flexographic printing. The standard applies to HAP present in

inks, ink extenders, solvents, coatings, varnishes, primers, adhesives,

and other materials applied with rotogravure and flexographic plates.

Printed items include magazines, advertising inserts, catalogs,

flexible packaging, corrugated boxes, paper towels, newspapers, wall

coverings, floor coverings, shower curtains, etc.

Sources in the publication rotogravure segment of the printing and

publishing industry include but are not limited to ink and solvent

storage tanks, ink mixing, printing, press and parts cleaning, proof

and production presses and solvent recovery. Sources in the product/

package rotogravure and wide-web flexography segments include the

printing presses.

Various organic HAP are used in the printing industry. Organic HAP

used include toluene, xylene, ethylbenzene, methyl ethyl ketone, methyl

isobutyl ketone, methanol, hexane, dibutylphthalate, toluene

diisocyanate, ethylene glycol and glycol ethers. These are the HAP

expected to be emitted by the industry, however, the proposed standards

apply to emissions of all organic HAP listed in section 112(b).

B. Proposed Standards for Affected Sources

In addition to the standards for affected sources as discussed

below, the affected sources would be subject to the General Provisions

which were promulgated in the Federal Register March 16, 1994 (59 FR

12408) under 40 CFR part 63, subpart A. The General Provisions

stipulate that all affected sources subject to the proposed rule are

also subject to, as appropriate, 40 CFR 63.4, 63.5, and 63.6.

The proposed rule requires each owner or operator who uses a

control device or equipment to control HAP emissions to prepare an

operation and maintenance plan in accordance with Sec. 63.6. In

addition to the information required in Sec. 63.6, the proposed rule

requires that the owner or operator of the control device or equipment

include the following information: (1) The operation and maintenance

criteria for each air pollution control device or equipment, including

a standardized checklist to document the operation and maintenance of

the equipment; (2) a systematic procedure for identifying malfunctions

and for reporting them [[Page 13669]] immediately to supervisory

personnel; and (3) procedures to be followed to ensure that equipment

or process malfunctions due to poor maintenance or other preventable

conditions do not occur.

The General Provisions also state that an owner or operator who

uses an air pollution control device or equipment not listed in the

proposed rule must submit to the Administrator for approval a

description of the device, test data verifying the performance of the

device or equipment for HAP and/or VOC emissions, appropriate operating

parameters that would be monitored to establish compliance with the

proposed standards, and a copy of the inspection and maintenance plan

required under Sec. 63.6. The authority to approve an alternate air

pollution control device is retained by the Administrator and is not

delegated.

Finally, Sec. 63.6(g) allows an owner or operator of an affected

source to use alternative means of compliance. This allows the

development and use of new technology not known or not demonstrated at

the time the rule was promulgated.

The affected sources for the proposed standards are defined as

follows: (1) Each publication rotogravure facility (all publication

rotogravure presses plus all associated operations including but not

limited to ink and solvent storage tanks, ink mixing, printing, press

and parts cleaning, proof and production presses and solvent recovery);

and (2) each product or packaging rotogravure or wide-web flexographic

press or group of presses controlled by a common solvent recovery

system. The following paragraphs summarize the proposed standards for

each affected source.

1. Publication Rotogravure Presses

The proposed standards for publication rotogravure facilities would

apply to all new and existing affected sources. The proposed standards

allow the use of control devices provided each facility achieves an

overall control efficiency, taking into account capture and control

device efficiency of 92 percent, when the organic HAP content of

solvent borne inks and other materials used is equivalent to the

volatile matter content. When non-HAP VOC or water is present in the

inks or other materials applied, each control device must achieve a

control efficiency such that the sum of the organic HAP recovered or

destroyed, plus the water used, plus the VOC used, minus the organic

HAP used makes up a minimum of 92 percent of the sum of the VOC used

plus the water used. (Organic HAP emitted is less than 8 percent of the

total volatile matter.)

Compliance with the proposed standard would be demonstrated by a

monthly mass balance when a solvent recovery system is used. Compliance

for control devices other than solvent recovery systems would be shown

on a continuous basis based on a specific operating parameter or

parameters, such as temperature for incinerators.

2. Package and Product Rotogravure and Wide-web Flexographic Presses

The proposed standards for package and product rotogravure and

wide-web flexographic presses would apply to all new and existing

affected sources. The proposed standards allow the use of low HAP

materials, control devices, or a combination of low HAP materials and

control devices. Presses applying any combination of inks, coatings,

primers, adhesives, solvents, extenders and other materials such that

the monthly mass weighted organic HAP contents of these materials is

equal to or less than 0.20 kg per kg of solids applied, or equal to or

less than 0.04 kg per kg of materials applied would be in compliance.

The proposed standards allow the use of control devices, provided that

each control device used for the control of HAP achieves an overall

control efficiency, taking into account capture and control device

efficiency of 95 percent. Presses would also be allowed to comply with

the proposed standards by using control systems provided that the HAP

emissions are equal to or less than 0.20 kg per kg of solids applied.

In cases where a solvent recovery system is used to control emissions

from more than one press, the group of commonly controlled presses can

be considered a single affected source for the purpose of complying

with the overall control device efficiency standard or the overall

organic HAP emission rate standard.

Compliance with the proposed standard would be demonstrated either

by a monthly mass balance or through the use of continuous emission

monitors when a solvent recovery system is used. Compliance for control

devices other than solvent recovery systems would be shown on a

continuous basis based on a specific operating parameter or parameters,

such as temperature for incinerators. Compliance with the proposed

organic HAP content level standards would be shown on a monthly basis

for compliant materials. Sources demonstrating compliance by a

combination of means would demonstrate control device efficiency as

described above and demonstrate mass average organic HAP content on a

monthly basis.

C. Compliance Dates

The proposed rule would require all existing sources to comply no

later than three years after the effective date of the standards. In

addition, the proposed rule adopts the compliance dates specified in

Sec. 63.6(b) and Sec. 63.6(c). New sources must comply with the

standard upon startup or the effective date of this regulation,

whichever is later.

D. Compliance Extensions

Because of the length of time necessary to properly specify, order

and install additional capture and control equipment some existing

facilities may need to request a compliance extension. Similarly, some

existing facilities choosing to adapt to lower HAP ink (and other press

material) formulations may have to select and test substitutes for a

large number of specific applications. These existing facilities may

need to request a compliance extension.

Section 63.6(i) of 40 CFR part 63 provides the requirements for

requesting an extension of compliance with a relevant standard

established under part 63. Specifically, Sec. 63.6(i)(4) allows the

issuance of a permit granting an extension of up to one year to comply

with the standard, if such additional period is necessary for the

installation of controls. Section 63.6(i)(4)(i)(B) requires requests

for compliance extensions to be submitted no later than 12 months

before the affected source's compliance date.

E. Compliance Testing and Monitoring

In addition to the specific testing and monitoring requirements

specified below for each affected source, the proposed rule adopts the

testing requirements specified in Sec. 63.7.

1. Test Methods and Procedures

a. Publication Rotogravure. For facilities using solvent recovery

systems, the overall control efficiency would be determined using a

mass balance over the period of each calendar month. Owners or

operators would be required to measure the amount of all materials used

during the month and to determine the organic HAP and volatile matter

content of these materials. Owners or operators would also be required

to measure the amount of volatile matter recovered by the solvent

recovery system during the month and to calculate the overall HAP

control efficiency. The organic HAP content would be determined by

proposed EPA Method 311, or from manufacturers data when these data are

equivalent to those obtained from proposed EPA Method 311. When it is

not possible to [[Page 13670]] determine the organic HAP content using

proposed EPA Method 311, the owner or operator shall submit to the

Administrator an alternative technique for determining the organic HAP

content. The volatile matter content of the materials used shall be

determined by manufacturers formulation data or by Method 24A of 40 CFR

part 60, appendix A.

For facilities using incinerators, owners or operators must

determine the incinerator destruction efficiency and the capture

efficiency. Incinerator destruction efficiency would be determined

using EPA Method 1 or 1A, EPA Method 2, 2A, 2C or 2D, EPA Methods 3 and

4, and EPA Method 25 or 25A of 40 CFR part 60, appendix A. Capture

efficiency would be confirmed using Procedure T to verify the presence

of a permanent total enclosure or determined using the capture

efficiency protocol specified in 40 CFR 52.741 (a)(4)(iii).

b. Package and Product Rotogravure and Wide-web Flexography. Owners

or operators may comply by means of use of materials meeting the

organic HAP threshold requirements or through use of control equipment,

or through a combination of low organic HAP materials and control

equipment. The proposed standards for organic HAP emissions would

require compliance with an organic HAP content threshold based on

solids content (kg of organic HAP per kg of solids applied), an organic

HAP threshold based on material (kg of organic HAP per kg of materials

applied), an overall organic HAP control efficiency (percent), or an

organic HAP emission rate (kg of organic HAP emitted per kg of solids

applied).

The organic HAP content of inks, coatings, primers, adhesives,

solvents and other materials applied on the press would be determined

by proposed EPA Method 311, or from manufacturers data when these data

are equivalent to those obtained from proposed EPA Method 311. When it

is not possible to determine the organic HAP content using proposed EPA

Method 311, the owner or operator shall submit to the Administrator an

alternative technique for determining the organic HAP content.

The facility may rely on manufacturer's data to determine the

organic HAP content when these data are equivalent to those obtained

from proposed EPA Method 311. The mass of each ink, coating, primer,

adhesive, solvent and other material applied would be determined using

company records. If diluent solvents or other ingredients are added to

a material prior to application, then the total organic HAP fractions

and mass must be adjusted appropriately to account for such additions.

These values would be required for each monthly period; however, only

changes in formulation would require re-determination of total organic

HAP weight fraction. The proposed standards would then require the

owner or operator to calculate the average mass of organic HAP in

materials applied per mass of solids applied.

If an owner or operator is seeking to comply by using materials

with a weighted average HAP content below the organic HAP content

threshold requirement or the low solids organic HAP threshold

requirement, the owner or operator would need to determine the organic

HAP content and solids content. If no changes in formulation as applied

occurred, then a re-calculation of the organic HAP level would not be

required.

If a control device is used, the proposed standards require the

owner or operator to demonstrate compliance with the overall control

efficiency requirement of at least 95 percent. Alternately, the owner

or operator may determine the overall control efficiency of the

equipment and the HAP content and solids content of the materials

applied. To comply by this combination of means, the owner or operator

would have to demonstrate a HAP emissions limitation of 0.20 kg HAP per

kg of solids applied.

For a solvent recovery system, overall control efficiency would be

determined using a liquid-liquid mass balance, or by conducting an

initial performance test of capture efficiency and using continuous

emissions monitors. The liquid-liquid mass balance determination would

be made every month. Owners or operators would be required to measure

the amount of all materials applied during the month and to determine

the volatile matter content of these materials. Owners or operators

measuring overall control efficiency using a liquid-liquid mass balance

would also be required to measure the amount of volatile matter

recovered by the solvent recovery system during the month and to

calculate the overall HAP control efficiency.

Owners or operators using solvent recovery systems may also

demonstrate compliance by conducting an initial performance test of

capture efficiency and operating continuous emissions monitors to

determine the total volatile matter content at both the inlet to and

the outlet from the carbon adsorber such that the percent efficiency of

the carbon adsorber can be calculated for each calendar month. The

owner or operator must verify the presence of a permanent total

enclosure using Procedure T, or determine the capture efficiency using

the protocol specified in 40 CFR 52.741(a)(4)(iii). The overall organic

HAP control efficiency must be calculated as the product of the capture

efficiency and the carbon adsorber efficiency.

For control devices other than carbon adsorbers, the overall

control efficiency would be based on capture efficiency and destruction

efficiency. Capture efficiency would be determined based on the

procedure specified in 40 CFR 52.741(a)(4)(iii), unless the operation

is performed within a permanent total enclosure. An enclosure that

meets the requirements of a permanent total enclosure as specified by

Procedure T of 40 CFR 52.741 would have a capture efficiency of 100

percent.

The destruction efficiency of a control device other than a carbon

adsorber would be determined using EPA Method 1 or 1A, EPA Method 2,

2A, 2C or 2D, EPA Methods 3 and 4, and EPA Method 25 or 25A of 40 CFR

part 60, appendix A. The owner or operator would record such process

conditions as may be necessary to determine the conditions of the

performance test.

To determine the value of an incinerator operating parameter that

will demonstrate continuing compliance, the time weighted average of

the values recorded during the performance test shall be computed. For

a thermal incinerator, the owner or operator shall establish as the

operating parameter the minimum combustion temperature. For a catalytic

incinerator, the owner or operator shall establish as the operating

parameters the minimum gas temperatures both upstream and downstream of

the catalyst bed. These minimum temperatures are the operating

parameters used to demonstrate continuing compliance.

The affected source is in compliance if the overall HAP control

efficiency is at least 95 percent. Alternately, the source can comply

on the basis of HAP emission limitation. The facility would be required

to determine the organic HAP content and solids content of inks,

coatings, primers, adhesives, solvents and other materials applied on

the press. The mass of each ink, coating, primer, adhesive, solvent and

other material applied would be determined using company records. If

diluent solvents or other ingredients are added to a material prior to

application, then the total organic HAP content, solids content and

mass must be adjusted appropriately to account for such additions.

[[Page 13671]]

The organic HAP content would be determined from proposed EPA

Method 311 or, when this is not possible the owner or operator shall

submit to the Administrator, an alternative technique for determining

the organic HAP content. Manufacturer's formulation data may be used

provided that the data are equivalent to those obtained using proposed

EPA Method 311. The volatile matter and solids content of the materials

used shall be determined by manufacturers formulation data or by Method

24 of 40 CFR part 60, appendix A.

These values would be required for each monthly period. The

proposed standards would then require the owner or operator to

calculate the average mass of organic HAP in materials applied per mass

of solids applied. The overall control efficiency as determined above

would be used to determine the HAP emission limitation. To comply by

this combination of means, the owner or operator would have to

demonstrate a HAP emissions limitation of 0.20 kg HAP per kg of solids

applied.

2. Monitoring Requirements

Monitoring is required by the proposed standards to determine

whether a source is in compliance. For owners or operators using

thermal or catalytic incinerators, this can be accomplished by

measuring site-specific operating parameters, the values of which are

established by the owner or operator during the initial compliance

test. The operating parameter value is defined as the minimum or

maximum value established for a control device or process parameter

that, if achieved by itself or in combination with other operating

parameter values, determines that an owner or operator is complying

with the applicable emission limitation or standards. This type of

monitoring would be required for those emission points for which the

standards are expressed as a percent control, or for affected sources

using control devices to achieve an organic HAP emission limit. In

addition, the owner or operator is expected to install and operate the

monitoring equipment properly.

The proposed rule would require temperature to be monitored, using

a continuous recorder, for incinerators. For catalytic incinerators,

temperature monitors would be placed immediately before and after the

catalyst bed. For other incinerators, the temperature monitor would be

placed in the firebox or in the ductwork immediately downstream of the

firebox and before any substantial heat exchange occurs. All monitoring

equipment would be installed, calibrated, maintained, and operated

according to manufacturer's specifications.

The proposed standards would require each owner or operator to

establish a range of values for each of these monitored parameters

during the initial performance test. As long as the control device is

operated within the established ranges, the proposed emission standards

are considered to be met. Consequently, exceedances of these parameters

would be considered a violation of the standards since operating the

control device outside of the established ranges may reduce the

efficiency of the control device.

Owners or operators of publication rotogravure sources operating

solvent recovery systems would be required to conduct monthly mass

balances as described in the section II.E.1 of the preamble. Owners or

operators of other sources operating solvent recovery systems would be

required either to conduct monthly mass balances as described in the

previous section or to operate continuous emission monitors. The

continuous emission monitors would be used to determine the total

volatile matter concentration at both the inlet to and the outlet from

the carbon adsorber, such that the percent efficiency of the carbon

adsorber can be calculated for each calendar month.

Owners or operators of package or product rotogravure or

flexographic printing facilities complying by means of use of materials

meeting the applicable HAP content threshold standards would

demonstrate compliance through recordkeeping as described in section

II.E.1 of the preamble.

Under 40 CFR 63.6(g), an owner or operator of an affected source

may request the use of alternative methods of emission reduction for

complying with design, equipment, work practice, or operational

emission standards, or combination thereof, established under this

part. Under the proposed rule, an owner or operator of an affected

source may also use control devices other than those specifically

identified in the proposed rule as a means for achieving compliance

with any portion of the rule. If devices other than those identified

are used, the proposed standards would require the owner or operator to

submit the parameters to be monitored to the Administrator for

approval. The authority to approve the use of alternate control devices

and the parameters to be monitored is retained by the Administrator and

is not delegated.

Section 114(a)(3) of the Act requires enhanced monitoring and

compliance certifications of all major stationary sources. The annual

compliance certifications certify whether compliance has been

continuous or intermittent. Enhanced monitoring shall be capable of

detecting deviations from each applicable emission limitations or

standard with sufficient representativeness, accuracy, precision,

reliability, frequency, and timeliness to determine if compliance is

continuous during a reporting period. The monitoring in this regulation

satisfies the requirements of enhanced monitoring.

F. Recordkeeping and Reporting Requirements

The proposed rule proposes to adopt the requirements contained in

40 CFR 63.9 and 40 CFR 63.10. The proposed rule, however, contains

additional or clarifying elements and changes certain time periods

allowed for submitting or responding to certain reports and requests

required in Sec. 63.10. These elements and changes are summarized below

for each of the operations for which standards are being proposed.

1. Recordkeeping Requirements

a. Publication Rotogravure. Records must be maintained of the

organic HAP and volatile matter content, as received, and the monthly

usage of all inks, solvents, varnishes, adhesives and other materials

applied on publication rotogravure presses. Where incinerators are

used, records must be maintained of the overall control efficiency and

all test results, data, and calculations used in determining the

overall control efficiency.

Where solvent recovery systems are used, records must be maintained

of the overall control efficiency, all test results, data, and

calculations used in determining the overall control efficiency, and

the monthly material balances used to demonstrate compliance.

b. Packaging and Product Rotogravure and Wide-web Flexography.

Records must be maintained of the organic HAP, volatile matter and

solids content, as received, and the monthly usage of all inks,

solvents, varnishes, primers, adhesives and other materials applied on

packaging and product rotogravure presses and wide-web flexographic

presses. Each owner or operator would be required to keep records of

the equipment monitoring parameter measurements specified in the

proposed rule. For an incinerator other than a catalytic incinerator,

continuous records must be maintained of the firebox temperature (or

temperature in the ductwork immediately downstream of the firebox). For

a catalytic incinerator, continuous records must be maintained

[[Page 13672]] of the gas stream temperature immediately before and

after the catalyst bed. For both types of incinerators, records must be

maintained of the overall control efficiency and all test results,

data, and calculations used in determining the overall control

efficiency.

For carbon adsorbers, records must be maintained of the overall

control efficiency, all test results, data, and calculations used in

determining the overall control efficiency.

2. Reporting Requirements

The proposed rule would require four basic types of reports: (1)

Initial notification, (2) notification of compliance status, (3)

periodic reports, and (4) other reports. In addition, the proposed rule

would require that the results of any performance test required under

Sec. 63.7 be reported no later than 60 days after the completion of the

test. A permit application as required under 40 CFR part 70 may be used

in lieu of the initial notification provided the same information is

contained in the permit application as required for the initial

notification.

As stated above, the proposed standards adopt the reporting

requirements contained in Sec. 63.9(a) through Sec. 63.9(e) and

Sec. 63.9(h) through Sec. 63.9(j) and 63.10 (a), (b), (d), and (f).

However, the time period allowed for the Administrator to notify the

owner or operator in writing of approval or disapproval of the request

for an adjustment to a particular time period or postmark deadline

submitted under Sec. 63.9(i) has been changed to within 30 calendar

days of receiving sufficient information to evaluate the request,

rather than 15 calendar days as provided for in Sec. 63.9(i)(3).

Sections 63.9 and 63.10 identify the type of generic information to

be included in the initial notification, notification of compliance

status, and other reports and, therefore, this information is not

repeated in this preamble. The following paragraphs summarize the

additional information specific to the printing and publishing rule

that should be included in the notification of compliance status and

the type of information to be included in the periodic reports.

a. Publication Rotogravure. The notification of compliance status

should identify the control devices that were used to demonstrate that

the facility was in compliance. Specific reporting requirements are

dependent on how an owner or operator chooses to comply with the

regulation. If solvent recovery systems are used and liquid-liquid

material balances are conducted, semiannual reports would be required

that contain information on all months when the material balances were

not in compliance with the standards.

If incinerators are used, semiannual reports would be required that

contain information on all days when any 3-hour average temperature was

below the average temperature established during the most recent

performance test during which compliance was demonstrated. The first

three hour period will commence when the affected source begins

operation or restarts following a shutdown period. Subsequent three

hour periods commence every three hours of operation. When an affected

source shuts down during a three hour period, the average temperature

for the period between the commencement of the three hour period and

shut down would be used for the purpose of compliance demonstration.

If incinerators are used, or if solvent recovery systems are used

but liquid-liquid material balances are not conducted, semi-annual

reports would be required that contain information on all days when for

any three hour period, the average value of the site-specific operating

parameter used to monitor capture system performance was greater than

or less than (as appropriate) the operating parameter value established

for the capture system.

If a semiannual report is required for the period covered by the

first semiannual report of the reporting year, a semiannual report

would be submitted for the following semiannual period even if no

exceedances occurred in that period. If no exceedances occur during the

entire reporting year, each owner and operator would submit annual

statements indicating that each affected facility has been in

compliance.

b. Packaging and Product Rotogravure and Wide-web Flexography. The

notification of compliance status should identify whether low-HAP

materials or control devices were used to demonstrate that the facility

was in compliance, and, for control devices and capture systems, what

operating parameters were identified for continuous monitoring in order

to ensure compliance with the proposed standards. Specific reporting

requirements are dependent upon how an owner or operator chooses to

comply with the regulation.

Owners and operators complying using low-HAP materials would be

required to report each exceedance of the organic HAP content level or

the low solids organic HAP content level. These reports would be

submitted on a semiannual basis.

If incinerators are used, semiannual reports would be required that

contain information on all days when any 3-hour average temperature was

below the average temperature established during the most recent

performance test during which compliance was demonstrated. The first

three hour period will commence when the affected source begins

operation or restarts following a shutdown period. Subsequent three

hour periods commence every three hours of operation. When an affected

source shuts down during a three hour period, the average temperature

for the period between the commencement of the three hour period and

shut down would be used for the purpose of compliance demonstration.

If solvent recovery systems are used, and the owner or operator

chooses to demonstrate compliance by means of a liquid-liquid mass

balance, semiannual reports would be required that contain information

on all months when the material balances were not in compliance with

the standards.

Owners or operators of affected sources complying with the HAP

emission limitation using a combination on control devices and low HAP

materials would be required to submit semiannual reports containing

information on control device exceedances as described above, in

addition to reports of exceedances of monthly calculated HAP emission

limitations.

If incinerators are used, or if solvent recovery systems are used

but liquid-liquid material balances are not conducted, semi-annual

reports would be required that contain information on all days when for

any three hour period, the average value of the site-specific operating

parameter used to monitor capture system performance was greater than

or less than (as appropriate) the operating parameter value established

for the capture system.

If a semiannual report is required for the period covered by the

first semiannual report of the reporting year, a semiannual report

would be submitted for the following semiannual period even if no

exceedances occurred in that period. If no exceedances occur during the

entire reporting year, each owner and operator would submit annual

statements indicating that each affected facility has been in

compliance. [[Page 13673]]

III. Summary of Environmental, Energy, and Economic Impacts of the

Proposed Standards

A. Emission Reductions

1. Existing Facilities

For the existing publication rotogravure printing industry (27

facilities), the nationwide baseline HAP emissions are estimated to be

17,500 Mg/yr (19,200 tpy). Implementation of the proposed regulation

would reduce these emissions by 4,750 Mg/yr (5,220 tpy), or 27 percent.

For the existing product and packaging rotogravure and wide web

flexographic printing industry (approximately 1,200 facilities), the

nationwide baseline HAP emissions are estimated to be 4,200 Mg/yr

(4,620 tpy). Implementation of the proposed regulation would reduce

these emissions by 1,940 Mg/yr (2,140 tpy), or 46 percent.

2. New Facilities

It is expected that any new facilities would be designed to meet

the proposed standards because of other federal, state and local

environmental and occupational safety regulations. No net emission

reduction from new facilities is expected as a result of the proposed

regulation.

B. Secondary Environmental Impacts

Secondary environmental impacts are considered to be any air,

water, or solid waste impacts, positive or negative, associated with

the implementation of the proposed standards. These impacts are

exclusive of the direct organic HAP air emission reductions discussed

in the previous section.

Most of the organic HAP are VOC. Capture and control of HAP which

is presently emitted will result in a decrease in VOC emissions. It is

expected that some product and packaging rotogravure and wide-web

flexographic facilities will comply with the proposed standard by

substituting non-HAP materials for HAP presently in use. In some cases,

the non-HAP materials will be VOC, however, in other cases, non-VOC (e.

g. water) materials will be used.

The use of newly installed or upgraded control devices will result

in greater electricity consumption. Increases in emissions of sulfur

dioxide, nitrogen oxides and carbon dioxide from electric utilities

could result. In the product and packaging rotogravure and wide-web

flexographic printing segments, some plants will comply by installing

or upgrading incinerators. Supplemental fuel, typically natural gas,

will be used, particularly for thermal incinerators. Combustion of this

fuel will result in additional carbon dioxide emissions and may result

in additional emissions of nitrogen oxides.

Facilities converting to waterborne materials as a means or partial

means of compliance may have reduced RCRA hazardous waste disposal if

the status of the waste ink changes from hazardous to nonhazardous. An

increase in wastewater discharge may occur if waste ink and waterborne

washup materials are discharged to publicly owned treatment works

(POTW). There is no assurance that facilities converting to low-HAP

formulations will adopt waterborne, rather than non-HAP VOC based

materials. While EPA expects wastewater and solid waste impacts in

general to be insignificant, it is aware of a frequent practice in the

printing and publishing industry of using shop towels for cleaning.

This generates a waste load which may be sent to industrial laundries

(and ultimately to POTW) in the case of cloth towels, or to landfills

in the case of disposable towels. EPA invites submission of comments

and data on how effluent from industrial laundries may be affected by

this regulation.

New and upgraded catalytic incinerators will require catalyst.

Catalyst life is estimated to be in excess of ten years. Spent catalyst

will represent a small amount of solid waste and in some cases the

spent catalyst will be regenerated by the manufacturer for reuse.

Activated carbon used in solvent recovery systems is returned to the

manufacturer at the end of its useful life and converted to other

salable products. No solid waste impact is expected from this source.

C. Energy Impacts

The operation of new and upgraded control devices will require

additional energy. Capture and control of increased volumes of solvent

laden air will require additional fan horsepower. Operation of

incinerators, particularly thermal incinerators will require

supplemental fuel (typically natural gas). Operation of solvent

recovery systems will require steam regeneration of the activated

carbon; boilers are typically fired with natural gas or fuel oil.

The total additional electrical energy required to meet the

proposed standard is estimated to be 55 million kilowatt-hours (kWh)

per year. This includes 32 million kWh for publication rotogravure, 20

million kWh for product and packaging rotogravure and 3.0 million kWh

for wide web flexography. Fuel requirements total 1.0 trillion Btu per

year. This includes 580 billion Btu for publication rotogravure, 370

billion Btu for product and packaging rotogravure and 58 billion Btu

for wide web flexography.

D. Cost Impacts

The total capital and annualized costs (1993 dollars) attributable

to compliance with the proposed standards have been estimated for

existing sources. It is expected that new facilities would meet the

proposed regulations as a result of other federal, state and local

environmental and occupational safety regulations.

1. Capital Costs

Capital costs would be incurred in upgrading existing capture and

control systems at those facilities presently operating control devices

that do not meet the proposed standards. Facilities which do not

presently operate control devices would be expected to capitalize a

period of downtime necessary to convert to low-HAP materials. Total

capital costs are estimated at $133 million. These costs include $92

million at publication rotogravure facilities for improved capture and

upgrades to solvent recovery systems to handle increased volumes of

pressroom air.

Capital costs at product and packaging rotogravure facilities are

estimated at $34 million. These costs include improved capture and

upgrades to control devices for facilities presently operating control

devices. For facilities not presently operating control devices the

costs are based on capitalized downtime.

Capital costs at wide-web flexographic facilities are estimated at

$7.2 million. These costs include improved capture and upgrades to

control devices for facilities presently operating control devices.

2. Annual Costs

Annual costs of the proposed standards have been estimated at $42

million per year. These costs include capital recovery over a ten year

period, operating costs for the newly installed and upgraded capture

and control systems, and costs for recordkeeping, reporting and

monitoring. These are net costs after taking into account the costs

presently being incurred for the baseline control level. The annual

costs include $21 million per year for publication rotogravure, $17

million per year for product and packaging rotogravure and $3.6 million

per year for wide-web flexography.

E. Economic Impacts

The preliminary economic impact analysis for the selected

regulatory alternative shows that the estimated [[Page 13674]] price

increases for printing products produced by the affected industries is

an average of 1.34 percent for those using publication and product/

packaging rotogravure presses, and less than 0.01 percent on average

for those using wide-web flexographic presses. The estimated decreases

in the quantity of printing production is an average of 3.85 percent

and 0.53 percent, respectively. No firms or facilities are at risk of

closures as a result of the standard.

For more information, consult the background information document.

IV. Process Descriptions and Control Technologies

A. Process Descriptions

1. Rotogravure Printing

Nearly all gravure printing is done by rotogravure. Gravure

printing is a printing process in which an image (type and art) is

etched or engraved below the surface of a plate or cylinder. On a

gravure plate or cylinder, the printing image consists of millions of

minute cells. Rotogravure requires very fluid inks which will flow from

the cells to the substrate at high press speeds. In addition to inks,

other materials including adhesives, primers, coatings and varnishes

may be applied with rotogravure cylinders. These materials dry by

evaporation as the substrate passes through hot air dryers.

Different colored inks, or other materials are applied in

succession as the web passes from station to station. A separate

cylinder, ink supply and dryer are required for each station. After the

ink is applied at each station, the web is dried before being printed

by the next station. Solvent borne or waterborne ink systems can be

used but these ink systems are not interchangeable. Both the printing

cylinders and the drying systems are specific to the ink system in use.

The evaporated components of the ink and other materials may contain

HAP to varying extents. Rotogravure can be divided into the publication

and product/packaging segments. Because of the expense and complexity

of rotogravure cylinder engraving, it is particularly suited to long

run printing jobs.

a. Publication Rotogravure. Publication rotogravure printing

focuses on magazine, catalog and advertising insert printing. All U. S.

publication rotogravure plants presently use toluene/xylene based ink

systems, and operate solvent recovery systems based on carbon

adsorption with steam regeneration. Recovered solvent is sold back to

the ink manufacturers. Press capture systems vary depending on the age

of the press. Typically, four stations are required to print each side

of the web. Publication rotogravure presses in operation in the U. S.

have up to 16 stations. It is generally believed in the industry that

publication rotogravure equipment is capable of higher quality printing

than competing processes.

The primary solvent in publication rotogravure ink is toluene, a

HAP. At some plants xylenes and ethyl benzene, also HAP, and non-HAP

aliphatic solvents are present in the solvent blend and are used,

emitted, recovered and handled in the same manner as toluene. The

plants purchase ink containing solvent and add additional solvent to

obtain the desired viscosity.

HAP emissions result from incomplete recovery of captured HAP, and

from incomplete capture. Activated carbon solvent recovery systems are

suitable for control of toluene and similar aromatic solvents. High

control efficiencies can be achieved, however some solvent is

unavoidably emitted as a result of thermodynamic limitations (the

toluene-carbon/toluene-air equilibrium) and flow irregularities (e.g.

channelling through the carbon bed). Some HAP is not captured in the

dryer exhaust. This includes HAP which evaporates from the ink

fountains into the pressroom, HAP which is evaporated from the web in

the dryers but is then swept out of the dryer as the web travels

towards the succeeding press station, HAP which remains in the web

after the last dryer which evaporates during additional processing

(slitting, folding, stitching, etc.) and HAP which leaves the plant

trapped in the magazine, catalog or advertising insert.

b. Packaging and Product Rotogravure. The rotogravure printing

operation is, in many cases, a relatively small part of the total

package or product production process. This section briefly describes

the various types of packages and products that include rotogravure

printing in their manufacture, and notes what production steps are

required in addition to the rotogravure printing step.

Folding Cartons. Folding carton packages are used for a wide

variety of products including wet and dry foods, beverages, bakery

items, and candy. They are also used for nonfood products such as

detergents, hardware, paper goods, cosmetics, medical products, tobacco

products, and sporting goods.

The folding carton is made from one of several grades of

paperboard. It may be printed, laminated or coated, or may be shipped

unprinted to be used with another label or wrapper. Besides printing,

operations in the manufacture of folding cartons include creasing,

trimming, die-cutting, coating, and gluing. The cartons are shipped

flat, to be assembled and filled by the customer.

Flexible Packaging. Flexible packaging materials start out as rolls

of paper or foil, or beads of plastic resin, and are ``converted'' into

a package or roll of packaging material. Flexible package manufacturers

are sometimes referred to as ``converters''. Converters produce a wide

range of non-rigid packages made of paper, plastic film, foil

laminates, and combinations of these substrates.

One portion of the flexible packaging industry provides fully

printed packaging materials (designated ``preformed specialty bags'')

to contract packagers. Another portion provides combination or

laminated materials (converted wrap) for printing and/or final packing

by captive packaging operations.

Labels and Wrappers. Labels and wrappers include roll and sheet

labels applied to cans, unprinted cartons, composite cans, bottles and

other containers, tags, and self-adhesive label products. Paper is the

common substrate, but laminates and foil are also used. The industry

makes a distinction between labels and wrappers, which are package

components, from a product that becomes the entire package and should

be called a flexible package.

Gift Wraps. About 90 percent of all gift wraps are printed. They

are produced by greeting card companies and by label and flexible

packaging firms. Rotogravure printing is particularly suitable for

producing the continuous patterns used on gift wrap.

Wallcoverings. The wallcovering industry is a traditional user of

rotogravure. The principal types of wallcoverings are prepasted paper,

prepasted paper-backed vinyl, fabric-backed vinyl, and specialty items

(e.g., metallics, grass cloth, rice paper). The steps in manufacturing

wallcoverings include printing the paper and laminating it to the

backing sheet.

Vinyl Printing. These products consist of auto upholstery,

furniture upholstery, tablecloths, decorative trim, and shower

curtains. Rotogravure dominates this product area because of the

complex repeat patterns (e.g., woodgrain), and the requirement, in many

cases, for overcoating that is readily applied using a rotogravure

cylinder. Printing is performed on unsupported vinyl, supported vinyl

(backed with fabric or paper), and paper substrate that is then coated

with vinyl. [[Page 13675]]

Decorative Laminates. These products consist of solid, thermoset

laminates used in furniture and construction, and other laminates,

principally wood grain veneers, widely used in furniture.

Floor Coverings. Rotogravure presses are used to decorate and apply

texture and finish to sheet vinyl floor coverings. Rotary screen

printing is sometimes used in combination with gravure. Rotogravure is

also used to print transfer papers used to decorate vinyl tile.

Tissue Products. Some type of printing process is used to apply

color patterns to paper towels, bathroom tissue, and napkins. The older

paper mills producing tissue products were typically equipped with

rotogravure presses.

Product and packaging rotogravure differs from publication

rotogravure with respect to the materials used, the applicable control

devices, and the decreased importance of the actual printing process in

an overall manufacturing process. Packaging and product rotogravure

printing uses a wide variety of different ink systems, including the

aromatic HAP based ink systems common to publication rotogravure,

solvent based non-HAP ink systems, and waterborne ink systems. Numerous

specially mixed colors are applied at various times in this industry

segment, in contrast to the publication segment which primarily applies

four basic colors. In addition, a wider range of materials are applied

with rotogravure cylinders in this segment of the industry. A variety

of coatings, adhesives and primers are applied at print stations on

rotogravure presses. Because of the variety of materials applied, the

approach to HAP and VOC control in packaging and product rotogravure

facilities varies. In addition to the activated carbon based solvent

recovery systems used by the publication segment, packaging and product

gravure facilities also use a variety of thermal and catalytic

oxidizers. Many facilities operate without significant HAP use and do

not have control devices.

In product and packaging rotogravure facilities, HAP is contained

in both the printing inks and in other materials (adhesives, coatings)

that are applied as part of a continuous manufacturing process. The

predominant type of ink is based on nitrocellulose resin, with some

polyamide inks. Solvent systems include aromatic, aliphatic and

oxygenated hydrocarbon solvent inks, and water-based inks.

2. Wide-Web Flexography

Flexographic printing is considered to be the application of words,

designs and pictures to a substrate by means of a printing technique in

which the pattern to be applied is raised above the printing plate and

the image carrier is made of rubber or other elastomeric materials. For

the purposes of the proposed regulation, flexographic presses capable

of printing substrates of 18 inches in width or greater are wide-web

flexographic presses. Because of the ease of plate making and press set

up, flexographic printing is more suited to short production runs than

gravure.

Flexographic inks must be very fluid to print properly.

Flexographic inks include both waterborne and solvent based systems.

Solvents used must be compatible with the rubber or polymeric plates;

thus, aromatic solvents are not used. Some of the components of solvent

based flexographic ink include ethyl, n-propyl and i-propyl alcohols;

glycol ethers, aliphatic hydrocarbons, and esters.

Wide web flexographic presses are used to print flexible and rigid

packaging; newspapers, magazines, and directories; paper towels,

tissues etc; and printed vinyl shower curtains and wallpaper.

Substrates include polyolefins, polystyrene, polyesters, glassine,

tissue, sulfite, kraft and other paper stocks, aluminum foil,

paperboard and corrugated cardboard.

Flexographic presses can be divided into three main types depending

on the relative relationship of the print stations. Stack presses have

individual print stations oriented vertically with the unwind and

rewind sections on the same side of the print stations. Stack presses

are easily accessible for rapid changeovers between press runs. Common

impression presses have the print stations around the circumference of

a single large impression cylinder. The web is constantly supported

between print stations, which is an advantage for printing on

stretchable materials. In-line presses have the print stations in a

horizontal row (the geometry is similar to rotogravure presses). Most

flexographic printing (including all flexographic newspaper and

corrugated carton printing) is done with waterborne inks. Waterborne

inks which contain no HAP are available for some applications. Some

waterborne inks contain relatively low proportions of HAP, principally

ethylene glycol and glycol ethers. Most solvent based flexographic inks

contain little or no HAP. Capture and control devices used with solvent

based inks are usually designed, permitted and operated for VOC

control.

B. Control Techniques

There are two approaches to limitation of HAP in the printing and

publishing industry. The first approach is to improve capture and

control systems or to add control devices where none are in use.

Capture and control can be addressed separately, although in many

cases, improved capture is achieved through an increase in the amount

of air handled. This can necessitate upgrades to existing control

devices. The second approach, focusing on pollution prevention, is to

substitute low HAP or HAP-free materials for materials (inks, coatings,

varnishes, adhesives, primers, etc.) presently in use.

1. Capture Systems

Capture systems are designed to collect solvent laden air and

direct it to a control device. In rotogravure and flexographic

printing, solvent is removed from the printed substrate by evaporation

in a dryer. The exhaust from the dryer can be ducted to a control

device. Additional systems are often used to collect solvents which

evaporate from other parts of the printing press, as well as those

which escape from the dryer. In addition, pressroom ventilation air can

be exhausted to a control device.

Differences in capture efficiency contribute much more to the

variation in overall efficiencies than the choice of control device.

Reported capture efficiencies ranged from estimates of less than 50

percent to the 100 percent capture which is assumed for systems meeting

the requirements of permanent total enclosures. Capture systems can be

improved through collection of additional solvent laden air from the

press area and through construction of additional hooding and press

enclosures. A capture efficiency of 100 percent can be assumed for

presses that meet the requirements of a permanent total enclosure.

a. Publication Rotogravure. Within the publication rotogravure

industry, all presses have dryer exhaust gases routed to the solvent

recovery system. Additional capture systems include dryer hood systems,

partial upper deck enclosures, full upper deck enclosures, enclosed

presses, permanent total enclosures, room enclosures, rooms operated

under negative pressure and floor sweeps. Typically, solvent laden air

captured from several presses is combined and treated with a common

solvent recovery system. The individual presses may have different

capture devices, and different capture efficiencies. [[Page 13676]]

b. Product and Package Gravure. In the product and package gravure

industry, many facilities use low VOC (and low-HAP) inks and coatings.

Dryer exhausts from these facilities may be captured and vented to the

atmosphere without the use of a control device. Where solvent based

inks are in use, more elaborate capture and control systems may be

present. Capture systems in use at product and packaging gravure

facilities include combinations of dryer exhausts, floor sweeps,

collection ducting, hoods, press enclosures, permanent total

enclosures, room enclosures, negative pressure pressrooms, partial

enclosures and ink pan covers. With the exception of permanent total

enclosures, none of these technologies has a precise definition with

regard to capture efficiency. In many cases terms are used

interchangeably. Where control devices are in use, solvent laden air

from several presses may be combined and ducted to a common control

device.

c. Wide-web Flexographic Printing. Capture systems in use at

flexographic printing facilities include combinations of dryer

exhausts, floor sweeps, hoods, and permanent total enclosures. Many

facilities, including most sheetfed corrugated box facilities have no

capture systems and rely on pressroom exhaust to the atmosphere to

dilute the small amount of HAP present in the ink.

2. Control Devices.

a. Carbon adsorbers. Adsorption systems are used to remove organic

compounds from gas streams when strict limits on the outlet

concentration must be met, or when recovery of the compound is desired.

Adsorption is effective on inlet concentrations ranging from a few

parts per billion to several thousand parts per million, and flow rates

of several hundred to several hundred thousand cubic feet per minute.

Carbon adsorbers typically have a removal efficiency of 95 to 99

percent.

Once the carbon reaches saturation, it can be regenerated with

steam within the adsorber vessel. This allows for the recovery of the

organic compounds for reuse.

b. Incinerators. Two basic types of incinerators, thermal and

catalytic, are used by package and product rotogravure and flexographic

printers to remove organic contaminants. Each type is discussed below.

(1) Thermal incinerators. Thermal incinerators can be generally

used on air streams with a wide concentration range of organics. These

control devices have minimal dependence on the characteristics of the

organic contaminants, so they can be used to control a wide variety of

emission streams. Thermal incinerators can achieve removal efficiencies

of 98 percent and higher.

The basic operation of thermal incinerators involves raising the

inlet air stream to the incineration temperature of the contaminants

and maintaining the temperature for a specific residence time. The

waste heat content of the incinerator exhaust stream is used to preheat

the inlet air stream. An auxiliary fuel is then typically required to

raise the air stream temperature to the incineration temperature.

(2) Catalytic incinerators. Catalytic incinerators are similar to

thermal incinerators except that they use a catalyst (a substance that

accelerates the rate of oxidation without undergoing a chemical change

itself) to assist in the oxidation of organic compounds to carbon

dioxide and water. The removal efficiency of catalytic incinerators can

be as high as 98 percent. Catalytic incinerators typically operate at

lower temperatures than thermal incinerators to achieve equivalent

efficiencies. For this reason, auxiliary fuel requirements and

operating costs are lower for catalytic incinerators than thermal

incinerators when used to control relatively dilute air streams.

V. Rationale for the Proposed Rule

A. Regulatory Development Process for NESHAP

During development of a NESHAP, the EPA collects information about

the industry, including information on emission source characteristics,

control technologies, data from HAP emission tests at well-controlled

facilities, and information on the cost, energy, and other

environmental impacts of emission control techniques. The EPA uses this

information in the development of possible regulatory approaches.

If the source category contains major sources, then a MACT standard

is required. Section 112(d)(3) of the Act defines the minimum

stringency requirements of the MACT standard for new and existing

sources. This level of control is referred to as the MACT ``floor,''

which needs to be determined as a starting point for developing the

regulatory alternatives.

Once the floor has been determined for new and existing sources for

a category or subcategory, the Administrator must set MACT standards

that are no less stringent than the floor level. Such standards must

then be met by all sources within the category or subcategory. However,

in establishing standards, the Administrator may distinguish among

classes, types, and sizes of sources within a category or subcategory

(section 112(d)(1) of the Act). Thus, for example, the Administrator

could establish two classes of sources within a category or subcategory

based on size and establish a different emission standard for each

class as long as each standard is at least as stringent as the floor.

The Act also contains provisions for regulating area sources. However,

except for certain recordkeeping requirements contained in the General

Provisions, these are not relevant to the proposed standards for

printing and publishing sources, which apply only to major sources.

The next step in establishing a MACT standard is the development

and analysis of regulatory alternatives. First, information about the

industry is analyzed to develop model plant populations for projecting

national impacts, including HAP emission reduction levels, costs, and

energy and secondary environmental impacts. Several regulatory

alternatives (which may be different levels of emission control,

different applicability criteria, or both, and one of which is the MACT

floor) are then evaluated to determine the most appropriate regulatory

alternative to reflect the MACT level.

In addition, although NESHAP are normally structured in terms of

numerical emission limits, alternative approaches are sometimes

necessary. Section 112(h) of the Act provides that if it is not

feasible to prescribe or enforce an emission standard, then a design,

equipment, work practice, or operational standard may be established.

For example, in some cases source testing may be impossible or at least

not practicable due to technological and economic limitations.

In the EPA's decision-making process, the regulatory alternatives

considered for new versus existing sources may be different and each

alternative must be technically achievable. In selecting a regulatory

alternative to represent MACT, the EPA considers the achievable

reduction in HAP emissions (and possibly other pollutants that are co-

controlled), the cost of control, and economic, energy, and other

nonair quality health and environmental impacts. The overall objective

is the achievement of the maximum degree of emission reduction without

unreasonable economic or other impacts.

The selected regulatory alternative is then translated into a

proposed regulation. The regulation implementing the MACT decision

typically includes sections addressing applicability, standards, test

methods and compliance [[Page 13677]] demonstration, monitoring,

reporting, and recordkeeping. The preamble to the proposed regulation,

published in the Federal Register, provides an explanation of the

rationale for the decision. The public is invited to comment on the

proposed regulation during the public comment period. Following an

evaluation of these comments, the EPA reaches a decision and

promulgates the final standards.

B. Determining Maximum Achievable Control Technology (MACT) ``Floors''

Once the EPA has identified the specific major source categories or

subcategories that it intends to regulate under section 112, MACT

standards are set at a level at least as stringent as the ``floor.''

Congress has provided directives to guide the EPA in the process of

determining the regulatory floor.

Congress specified that the EPA must establish standards which

require ``the maximum degree of reduction in emissions of the hazardous

air pollutants * * * that the Administrator * * * determines is

achievable * * *'' (section 112(d)(2) of the Act). In addition,

Congress limited the Agency's discretion by defining the minimum

baseline (floor) at which standards may be set, as follows:

(1) For new sources, the standards for a source category or

subcategory ``shall not be less stringent than the emission control

that is achieved in practice by the best controlled similar source, as

determined by the Administrator,''; and

(2) For existing sources, the standards ``may be less stringent

than standards for new sources * * * but shall not be less stringent,

and may be more stringent than: (A) the average emission limitation

achieved by the best performing 12 percent of the existing sources (for

which the Administrator has emissions information) * * * or (B) the

average emission limitation achieved by the best performing 5 sources *

* * for categories or subcategories * * * with fewer than 30 sources''

(section 112(d)(3) of the Act).

C. Selection of Pollutants and Source Category(ies)

Section 112(b) of the Act lists the HAP to be regulated with

standards established under section 112. Section 112(d), as amended,

requires the EPA to promulgate emission standards for each category or

subcategory of major sources and area sources of the HAP listed in

section 112(b). For the purpose of developing these standards, the EPA

may distinguish among classes, types, and sizes of sources within a

category or subcategory. The NESHAP are to be developed to control HAP

emissions from both new and existing sources pursuant to section 112(c)

of the Act.

The initial source category list (57 FR 31576, July 16, 1992),

required by section 112(c) of the Act, identifies source categories for

which NESHAP are to be established. This list includes all major source

categories of HAP known to the EPA at this time, and all area source

categories for which a finding of adverse effects warranting regulation

has been made.

The source category list identifies ``Printing/Publishing (Surface

Coating)'' as a source category because it contains major sources which

have the potential to emit at least 10 tons of any one HAP or at least

25 tons of any combination of HAP annually.

The printing and publishing industry encompasses printing by a

variety of graphic arts techniques applied to a variety of substrates.

Printing operations are included as one or more steps in the overall

manufacturing process for a wide variety of end products. Packaging and

product printing often makes up only a small part of the value of the

end product. For purposes of this rule, the EPA has defined the source

category as consisting of all facilities engaged in publication

rotogravure and product and packaging rotogravure and wide-web

flexographic printing.

D. Selection of Emission Points Covered by the Proposed Rule

The proposed rule would limit organic HAP emissions that result

from publication rotogravure and product and packaging rotogravure and

wide-web flexographic printing. The standard applies to HAP present in

inks, ink extenders, solvents, coatings, varnishes, primers, adhesives,

and other materials applied on publication rotogravure and product and

packaging and wide-web flexographic presses. Emission points in the

publication rotogravure segment of the printing and publishing industry

include but are not limited to ink and solvent storage tanks, ink

mixing, printing, press and parts cleaning, proof and production

presses and solvent recovery. Within the product/package rotogravure

and wide-web flexography industry the standard applies to inks and all

other materials applied with rotogravure or wide-web flexographic

printing presses.

A discussion of the rationale for including or excluding basic

processes from this proposed rule is given below.

1. Operations for Which Standards Are Being Proposed

EPA is proposing organic HAP emission standards for rotogravure and

wide-web flexographic printing operations. Within the publication

rotogravure segment of the industry, all organic HAP emitting

operations are covered by the standard. Current industry practices

instituted for compliance with applicable regulations pertaining to VOC

emissions include accounting for solvent use on a facility-wide or

control system wide basis determined by a periodic liquid-liquid mass

balance. Organic HAP emissions at points other than production printing

presses are relatively minor compared to press emissions. These

operations, including ink storage and mixing, parts cleaning and proof

presses can be controlled or uncontrolled provided that the overall

facility or control system meets the proposed standard. Based on

information provided by all U.S. publication rotogravure facilities,

there are readily available techniques to achieve substantial organic

HAP emissions reduction from the presses. Adequate information is

available to establish MACT for these facilities.

Within the product and packaging rotogravure and wide-web

flexographic printing segment of the industry, emission of organic HAP

from rotogravure and flexographic presses is covered.

Based on the information obtained from the industry in response to

information collection requests, in addition to information provided

voluntarily and during meetings with industry trade organizations,

there are several readily available techniques (including carbon

adsorption and thermal and catalytic incineration) to achieve

substantial emission reductions in these operations. While inks and

other materials containing organic HAP are being used at many

facilities, alternative formulations containing no organic HAP, or very

low concentrations of organic HAP are available for many specific

applications. Adequate information exists for establishing MACT for

capture and control devices and for alternate low-HAP formulations.

2. Excluded Operations

a. Inorganic HAP Emissions. Inorganic HAP are present in pigments

and film forming components of some inks. These components make up less

than 1 percent of the total HAP content of the materials. These

components remain on the substrate for the life of the publication,

product or package and are not expected to be emitted to the air.

b. Non-press Operations at Product and Packaging Rotogravure and

Wide-web Flexographic Printing Facilities. Operations related to press

and parts cleaning, proof presses, ink mixing and

[[Page 13678]] storage, film lamination and flexographic platemaking

have the potential to emit organic HAP. Organic HAP emissions from

these operations make up only a small fraction of HAP emissions from

the presses. Very few data are available regarding the extent of

emissions from these sources and applicable control techniques.

Adequate information is not available to establish MACT for these

potential emission points.

EPA is not proposing regulations at this time pertaining to off-

line rotogravure coating because these emission points will be covered

in a future standard for ``Paper and Other Web Coating''.

c. Narrow-web Flexography. Thousands of narrow web flexographic

printing facilities exist which primarily print tags and labels. No

major sources of this type have been identified based on a search of

the Toxic Release Inventory System, and it is unlikely that there are

any such facilities. Very few data are available regarding the extent

of emissions from these sources and applicable control techniques.

Narrow web flexographic printing facilities are typically very small

and predominantly use low HAP, low VOC inks. Adequate information is

not available to establish MACT for these potential emission points.

E. Selection of the Basis for the Proposed Rule

Section 112 of the Act defines a major source as any stationary

source or group of stationary sources located within a contiguous area

and under common control that emits or has the potential to emit

considering controls, 9.1 Mg/yr (10 tpy) or more of any one HAP or 22.7

Mg/yr (25 tpy) or more of any combination of HAP. The Act states that

new major sources must achieve the maximum achievable control

technology (MACT), which is the level of emission control already

achieved in practice by the best controlled similar source. The Act

further states that emission standards promulgated for existing sources

may be less stringent than standards for new sources; however,

standards for existing sources must not be less stringent than the

average emission limitation achieved by the best performing 12 percent

of the existing sources.

For all operations being covered by the proposed rule, the EPA has

determined that, taking into account nonair quality health and

environmental impacts, and energy impacts, MACT is equal to the MACT

floors for both existing and new sources. In addition, MACT for new

sources was found to be equal to MACT for existing sources. The EPA has

determined that no further emission reductions can be achieved for new

sources through the use of demonstrated technology than the level of

reduction represented by MACT for existing sources.

To evaluate the regulatory alternatives, model plants were

developed based on market segment (publication rotogravure, package and

product rotogravure and wide-web flexography), and size. These

characteristics were examined to determine whether any technological

justification existed to differentiate the proposed standards by market

segment or size. Based on this examination, the EPA has decided that

different market segments operate in different ways and that there is

justification to differentiate between the two market segments

identified on the basis of these characteristics. No compelling reasons

were identified as to why a facility of one size could not incorporate

the technology used by a facility of another size.

1. Publication Rotogravure.

Data were obtained from all of the 27 U. S. publication rotogravure

facilities. All of the control systems employ activated carbon based

solvent recovery systems. All facilities calculate overall efficiencies

on the basis of liquid-liquid mass balances. All facilities use toluene

based ink systems, although some facilities have replaced a portion of

the toluene with non-HAP organic solvents. Waterborne ink systems are

not technically feasible at this time for the high quality, high speed

printing which these facilities produce.

The average emissions limitation achieved by the best performing 5

facilities was 92 percent. This limitation is based on the level of

control achieved in each of twelve monthly material balances at the 5

plants with the best annual solvent recovery rates. The solvent

recovery data were analyzed on a plantwide basis. Some facilities

operated more than one solvent recovery system and it was not possible

to reliably isolate the individual systems. Annual average emission

limitations were higher, and facilities meeting the standard each and

every month will achieve annual emissions limitations of 92 percent or

greater.

To achieve 92 percent solvent recovery each month, a facility may

need a permanent total enclosure and an efficient solvent recovery

system. No more efficient alternative technologies are available.

Higher solvent recovery rates may not be achievable on a consistent

basis due to month-to-month variations in solvent accounting and due to

solvent retention in the printed substrate. Therefore the floor for new

sources was determined to be the same as the floor for existing sources

and no more stringent regulatory alternatives were found to exist.

2. Package and Product Rotogravure and Wide-web Flexography

Data were obtained from approximately 103 product and package

rotogravure printing facilities, and approximately 500 wide-web

flexographic facilities. Industry representatives believe that there

are approximately 400 product and package rotogravure facilities

operating in the U.S. There are approximately 800 wide-web flexographic

printing facilities in the United States. Different types of

incinerators and solvent recovery systems were operated by 146 of the

reporting facilities. The balance of the facilities had no control

device. In all cases where control devices were in operation, they were

designed and operated to control VOC emissions. It is assumed that the

performance of these control devices with respect to VOC and organic

HAP is equivalent.

The same types of control devices and capture systems were

generally applicable even though the materials applied, products,

substrates, and web widths of the controlled presses varied

considerably. The overall control efficiency data for the facilities

with the greatest emissions limitations were generally provided based

on tests conducted to comply with permit conditions. Where permanent

total enclosures were in place, capture efficiencies of 100 percent

were assumed and tests across control devices were conducted. The

emissions limitation achieved by the average of the best controlled 12

percent of the facilities was 95 percent.

To achieve 95 percent control of organic HAP a facility may need to

operate a permanent total enclosure and an efficient control device. At

present there are no technologies which can consistently achieve a

greater overall control efficiency than this. For this reason, the

floor for new sources was determined to be equal to the floor for

existing sources and no more stringent regulatory alternatives were

found to exist.

F. Selection of the Format of the Proposed Rule

Emission standards for control of HAP have been prescribed in

accordance with section 112(d) of the Act. Where control devices are in

place, emissions standards are proposed on the basis of

[[Page 13679]] overall efficiency, taking into account both capture and

control device efficiencies.

To encourage the use of non-HAP materials in the publication

rotogravure industry as an alternative to toluene (and ethylbenzene and

xylene) based materials, an alternate means of compliance allows credit

for 100 percent recovery of that portion of the solvent which is

replaced with non-HAP compounds. Thus, a facility achieving 90 percent

overall efficiency, using a solvent system which is 70 percent toluene

and 30 percent non-HAP solvent would comply on the basis of an

equivalent emissions limitation of 93 percent.

Based on the potential HAP content of the materials applied by the

best controlled 12 percent of the product and package rotogravure and

wide-web flexographic printing facilities, alternate standards were

proposed yielding equivalent emissions limitations. Sources applying

materials containing 0.20 kg organic HAP or less per kg of solids

applied on package and product rotogravure and wide-web flexographic

presses will not be required to operate a control device to comply with

the standard. Facilities operating systems with overall efficiencies

less than 95 percent would be able to comply by limiting the HAP

content of the inks, coatings, primers, adhesives, solvents, and other

materials applied such that the HAP emissions from the affected source

are 0.20 kg per kg of solids applied or less.

Certain press lines are used to apply low solids materials which

contain relatively low proportion of organic HAP relative to the mass

of material applied. Sources applying materials containing 0.04 kg

organic HAP per kg of material applied will not be required to operate

a control device to comply with the standard.

G. Selection of Emission Test Methods and Monitoring Requirements

1. Emission Test Methods

In addition to the specific test methods described below for

affected sources, the proposed rule adopts the provisions specified in

40 CFR 63.7.

a. Publication Rotogravure. Where a carbon adsorber is used, the

EPA is proposing to use a mass balance procedure for determining the

overall control efficiency. The proposed rule contains procedures as

specified in 40 CFR 60.433 for using a mass balance approach that would

calculate the amount of organic HAP and VOC applied and the amount

recovered. This information would then be used to calculate the overall

control efficiency of the carbon adsorber.

In determining compliance with the alternate standard for sources

that have substituted non-HAP VOC for a portion of the HAP in their

ink, the EPA is proposing that Method 24A be used for determining the

volatile matter content. This is a long-standing method for such

determinations. This determination may be conducted by the manufacturer

and provided to the owner or operator. The EPA is proposing that the

organic HAP content level be determined by proposed EPA Method 311.

This method was proposed (see Solicitation of Comments) as part of the

NESHAP for Wood Furniture Manufacturing Operations on December 6, 1994

(59 FR 62652). The EPA requests comment on the suitability of Method

311 for determination of HAP used in the printing industry.

b. Package and Product Rotogravure and Wide-web Flexography. If

control devices (e.g., incinerators, carbon adsorbers) are used the

proposed standards require them to achieve an overall control

efficiency of at least 95 percent, or a HAP emission limitation of no

more than 0.20 kg HAP per kg solids applied. It is necessary,

therefore, to identify the capture efficiency of the capture system,

the destruction or recovery efficiency of the control device, and,

where feasible, operational parameters that would be monitored to

ensure continuous compliance. The proposed standards also include

provisions for determining the capture and removal efficiencies. The

test methods and procedures being proposed for determining the capture

and removal efficiencies are those that are typical for control

devices.

The EPA is proposing that capture efficiency be determined by one

of two methods depending on whether or not the capture system is a

permanent total enclosure or not. A permanent total enclosure would be

verified according to the provisions specified in 40 CFR 52.741,

appendix B, Procedure T (and, thus would have a capture efficiency of

100 percent). The capture efficiency of all other systems would be

determined according to the procedures specified in 40 CFR

52.741(a)(4)(iii).

The EPA is proposing that the removal efficiency of a control

device be determined based on three runs, each run lasting one hour.

Method 1 or 1A of 40 CFR part 60, appendix A, as appropriate, would be

used for selection of the sampling sites, and the gas volumetric flow

rate would be determined using Methods 2, 2A, 2C, or 2D of 40 CFR part

60, appendix A, as appropriate. Method 25 or 25A of 40 CFR part 60,

appendix A, would then be used to measure either the organic

concentration or the total organic HAP concentration before and after

the control device. Alternatively, any other test method or data that

has been validated according to the applicable procedures in Method 301

of 40 CFR part 63, appendix A, may be used.

Owners or operators complying with the standard on the basis of

average HAP content of materials applied on the press would be required

to determine the HAP content of each material applied. The EPA is

proposing that the organic HAP content level be determined by proposed

EPA Method 311. This method was proposed (see Solicitation of Comments)

as part of the NESHAP for Wood Furniture Manufacturing Operations on

December 6, 1994 (59 FR 62652).

2. Monitoring Requirements

In accordance with paragraph (a)(3) of section 114 of the Act,

monitoring of stationary sources is required to determine the

compliance status of the sources, and whether compliance is continuous

or intermittent. Enhanced monitoring shall be capable of detecting

deviations from each applicable emission limitations or standard with

sufficient representativeness, accuracy, precision, reliability,

frequency, and timeliness to determine if compliance is continuous

during a reporting period. The monitoring in this regulation satisfies

the requirements of enhanced monitoring.

For affected sources complying with the proposed standards through

the use of control devices, initial compliance is determined through

the initial compliance test, and ongoing compliance through continuous

monitoring. The EPA has proposed the parameters to be monitored for

certain types of control devices now used in the industry. The values

of these parameters that correspond to compliance with the proposed

standards are set by the owner or operator during the initial

compliance test. If future monitoring indicates that control equipment

is operating outside of the range of values established during the

initial performance test, then the owner or operator is out of

compliance with the proposed standards, except as specified for

malfunctions in 40 CFR 63.6(e)(3).

Owners or operators using incinerators, and owners or operators

using solvent recovery systems and demonstrating compliance with

continuous emissions monitoring must identify the operating parameter

to be monitored to ensure that the capture efficiency measured during

the initial [[Page 13680]] compliance test is maintained, and conduct

monitoring of this parameter in accordance with the plan submitted with

the compliance status report. If future monitoring indicates that

capture system is operating outside of the range of values established

during the initial performance test, then the owner or operator is out

of compliance with the proposed standards, except as specified for

malfunctions in 40 CFR 63.6(e)(3).

a. Publication Rotogravure Sources Using Solvent Recovery Systems.

Publication rotogravure facilities operating solvent recovery systems

would be required to demonstrate continuing compliance by conducting a

liquid-liquid mass balance each and every month.

b. Other Sources Complying by Means of a Control Device. Product

and packaging rotogravure and wide-web flexographic sources complying

by means of a solvent recovery system would be required to demonstrate

continuing compliance either through the use of continuous emission

monitors or by conducting a liquid-liquid mass balance each and every

month.

Sources complying through the use of a thermal incinerator would be

required to install, calibrate, operate and maintain a temperature

monitoring device equipped with a continuous recorder to monitor the

temperature in the combustion chamber downstream of the combustion

zone. Sources complying through the use of a catalytic incinerator

would be required to install, calibrate, operate and maintain a

temperature monitoring device equipped with a continuous recorder to

monitor the temperatures at the inlet to the catalyst bed and the

outlet from the catalyst bed.

The rationale for selecting the control device parameters for

thermal and catalytic incinerators in this proposed rule is long

standing, and for more information see the proposal notice for the

SOCMI reactor processes NSPS (55 FR 26966 through 26969, June 29,

1990). The EPA is, therefore, simply proposing to adopt the same

monitoring parameters as have been required for previous standards.

H. Selection of Recordkeeping and Reporting Requirements

1. Recordkeeping

In addition to the specific recordkeeping requirements described

below for each affected source, the proposed rule adopts the provisions

specified in Sec. 63.10 (a), (b), (c)(1), (c)(5-8), (c)(10-15), (d)(1-

2), (d)(4-5), and (f). These were the only paragraphs from Sec. 63.10

that were considered to be applicable to the proposed rule.

Each owner or operator would be required to maintain records of

each applicability determination as described above in section II. A.,

each continuous monitoring system operated as described above in

section V. G., and each liquid-liquid mass balance as described above

in section V.

G. These Records Would Be Maintained in Accordance With the

Requirements of Sec. 63.10(b)

As called for by the General Provisions, each owner or operator of

an affected source would be required to develop a start-up, shut-down,

and malfunction plan, and keep it on record to be made available for

inspection, upon request, by the Administrator for the life of the

affected source or until the affected source is no longer subject to

the provisions of the proposed rule.

If an owner or operator of a product or packaging rotogravure or

wide-web flexographic source elects to comply on the basis of use of

low HAP materials, or on the basis on HAP emission limitation, the EPA

is proposing that records of the monthly mass-weighted average organic

HAP content for all inks, coatings, primers, adhesives, solvents and

other materials applied on the press be kept as well as all of the data

and calculations used to calculate these values. This would include the

mass and organic HAP content as applied of each material. This level of

information is required for an inspector to determine whether the

facility was in compliance and whether the proper data and calculations

were being used.

If a thermal or catalytic incinerator is used, each owner or

operator would be required to keep a record of the control device

operating parameters being monitored. Since for some control devices

compliance with the proposed standards is dependent on the control

device being operated properly, these records are necessary to

determine compliance. Specifically, a source would be out of compliance

if the recorded parameters were out of range. Thus, the EPA is

requiring these records for compliance determinations.

2. Reporting Requirements

In addition to the specific reporting requirements described below

for each affected source, the proposed rule adopts the provisions

specified in Sec. 63.9(a) through Sec. 63.9(e) and Sec. 63.9(g) through

Sec. 63.9(j) and Sec. 63.10 (a), (b), (d), and (f).

The proposed rule would require an owner or operator to submit the

following five types of reports:

(1) Initial notification,

(2) notification of performance tests and continuous emission

monitor evaluation periods,

(3) notification of compliance status,

(4) periodic reports, and

(5) other reports.

The purpose and contents of each of these reports are described in

this section. The wording of the proposed rule requires all reports to

be submitted to the ``Administrator.'' The term Administrator refers

either to the Administrator of the EPA, an EPA regional office, a state

agency, or another authority that has been delegated the authority to

implement this rule. In most cases, reports will be sent to state

agencies. Addresses are provided in the General Provisions of 40 CFR

part 63, subpart A.

Records of reported information and other information necessary to

document compliance with the regulation are required to be kept for 5

years. As required under the General Provisions, the two most recent

years must be kept on-site; the other three years may be kept off-site.

Records pertaining to the design and operation of the control and

monitoring equipment must be kept for the life of the equipment.

a. Initial Notification. The proposed standards would require

owners or operators who are subject to this subpart to submit an

initial notification. As outlined in the General Provisions under

Sec. 63.9, this report serves two basic purposes: (1) Notifies the EPA

that an existing facility is subject to the proposed standards and (2)

notifies the EPA of the construction of a new facility. A respondent

must also report any facility modifications as defined in Sec. 63.5.

This report will include the mass of HAP used at the facility during

the previous twelve months, as well as the mass of HAP expected to be

used at the facility during the next twelve months.

This report will establish an early dialogue between the source and

the regulatory agency, allowing both to plan for compliance activities.

The notice is due no later than 120 days after the effective date of

the proposed standards. Under the proposed rule, the initial

notification is not required from any source that has submitted a

permit application under title V of the Act, provided that the permit

application has been submitted by the same due dates as for the initial

notification and that the state to which the permit application has

been submitted has a permit program in place and has received

delegation of authority from the EPA.

b. Notification of Performance Tests and Continuous Emission

Monitor [[Page 13681]] Evaluation Periods. As adopted through the

General Provisions, Sec. 63.7 and Sec. 63.9(g), owners or operators

would be required to notify the Administrator in advance of conducting

performance tests of control devices and evaluating continuous

emissions monitors.

c. Notification of Compliance Status. As adopted through the

General Provisions, owners or operators who are subject to this subpart

would be required to submit a notification of compliance status. This

report contains the information necessary to demonstrate that

compliance has been achieved, such as the results of performance tests,

and average organic HAP contents, as well as the methods that will be

used for determining continuing compliance as outlined under Sec. 63.9.

Another type of information to be included in the notification of

compliance status is the specific range of each monitored parameter for

each affected source, the rationale for why this range indicates

compliance with the emission standard, and whether each source has

operated within its designated operating parameters. The report would

be due within 60 days after the final compliance date as specified in

the General Provisions.

d. Periodic Reports. The EPA is proposing to adopt a standard basis

for submitting periodic reports for each of the operations for which

standards are being proposed. Semiannual reports would be required

whenever an operation was found to be in non-compliance or whenever a

monitored parameter exceeded its value. For example, for a publication

rotogravure source, a semiannual report would be triggered for any

monthly period covered by the semiannual report in which the overall

efficiency of the solvent recovery system failed to meet the standard.

Semiannual reports would also be required whenever a change

occurred at a facility that might affect a source's compliance status

or that introduces a new element to the operation that was required to

be reported in the notification of compliance status. For example,

conversion of a press requiring a control device to operate with low-

HAP materials would require monthly averaging of materials applied to

maintain compliance. This change in compliance status would trigger a

semiannual report. For operations that did not experience any

exceedances or changes, the EPA is proposing that annual reports be

submitted to this effect.

The EPA is proposing to adopt the above schedule of reporting

because it provides a fair balance between the need to know certain

information in a timely fashion and reduces the burden to industry and

provides consistency within this regulation. The following paragraphs

discuss in more detail the specific types of information to be included

in these various periodic reports. The information being requested is

that which the EPA believes is necessary in the enforcement of the

proposed rule.

(1) Sources Operating Solvent Recovery Systems. A semiannual report

would be required whenever a monthly liquid-liquid mass balance failed

to meet the standard. Owners or operators choosing to demonstrate

compliance using CEM would be required to submit a semiannual report

for any semiannual period in which the calculated average efficiency,

including capture efficiency and control device efficiency failed to

meet the standard during any three hour period.

(2) Sources Operating Thermal and Catalytic Incinerators. A

semiannual report would be required for any semiannual period when a

monitored temperature parameter, averaged over a three hour period,

falls outside its appropriate range during any three hour period. A

semiannual report would be required for any semiannual period when a

monitored site-specific capture system parameter, averaged over a three

hour period, falls outside its appropriate range during any three hour

period.

(3) Package and Product Rotogravure and Flexographic Sources

Complying by Means of Low-HAP Materials. A semiannual report would be

required for any semiannual period in which the materials applied, when

averaged over a monthly period, exceed the standard for organic HAP

content based on solids applied or on materials applied during any

month.

e. Other Reports. The only ``other reports'' in the proposed rule

are those that are required under the General Provisions, subpart A of

40 CFR part 63. Of particular note is the report required in response

to periods of startup, shutdown, and malfunction. When the procedures

used during such periods are completely consistent with the plan, a

report stating such is to be delivered or postmarked by the thirtieth

(30th) day following the end of each calendar half. If the procedures

are not completely consistent with the plan, an owner or operator is to

report the actions taken within 2 working days after commencing actions

inconsistent with the plan, followed by a letter within 7 working days

after the end of the event.

I. Selection of Compliance Deadline

The proposed standards would require the owner or operator of an

existing rotogravure or wide-web flexographic printing operation to

comply with these standards within three years after they are

promulgated in the Federal Register. Section 63.7(a)(2) of the General

Provisions then allows a source 180 days after the compliance date to

demonstrate compliance through an initial performance test. A shorter

compliance time was not selected because the proposed timeframe is

necessary for those sources that will be required to install new

capture and/or control devices to purchase and install the equipment.

The proposed timeframe will also provide the greatest opportunity for

developing and adopting low HAP content materials. Administrative

procedures are established in Sec. 63.6(i) to implement compliance

extensions for existing sources that are unable to install controls by

the required compliance dates.

Owners or operators of new sources that commence construction after

the standards are proposed but before the standards are promulgated

will have to comply immediately upon startup, unless the promulgated

regulation is more strict than the proposed regulation. In accordance

with Section 112(i)(2) of the Act, if the promulgated standards are

more stringent than the proposed standards, the compliance date for

construction after proposal but before promulgation will be 3 years

after the promulgation date, provided the owner or operator complies

with the standards as proposed until the compliance date. The owner or

operator would then be required to conduct a performance test within

120 days after the compliance date. All other new sources will have to

comply with the proposed standards immediately upon startup.

J. Operating Permit Program

Under 40 CFR part 70, all major sources of HAP will be required to

obtain an operating permit. Emission limits, monitoring, and reporting

and recordkeeping requirements are typically scattered among numerous

provisions of State implementation plans (SIP's) or Federal

regulations. As discussed in the rule for the operating permit program,

this new permit program would include in a single document all of the

requirements that pertain to a single source. Once a state's permit

program has been approved, each printing and publishing facility that

is a major source within that state [[Page 13682]] must apply for and

obtain an operating permit. If the state wherein the printing and

publishing facility is located does not have an approved permitting

program, the owner or operator of a printing and publishing facility

must submit a part 71 permit application if requested under 40 CFR part

71.

K. Pollution Prevention Considerations

The Pollution Prevention Act of 1990 establishes the following

management hierarchy as national policy:

1. Pollution should be prevented or reduced at the source whenever

feasible;

2. Pollution that cannot be prevented should be recycled in an

environmentally safe manner whenever feasible;

3. Pollution that cannot be prevented or recycled should be treated

in an environmentally safe manner whenever feasible; and

4. Disposal or other release into the environment should be

employed only as a last resort and should be conducted in an

environmentally safe manner.

The Pollution Prevention Act considers ``source reduction'' a

fundamental aspect of pollution prevention. Source reduction is any

practice that reduces the amount of any hazardous substance entering

the waste stream or otherwise released into the environment prior to

recycling, energy recovery, treatment, or disposal. Practices such as

recycling, energy recovery, treatment, and disposal are not considered

pollution prevention measures under the Pollution Prevention Act.

The proposed rule provides strong incentives for pollution

prevention. Within the publication rotogravure segment, substitution of

non-HAP materials for organic HAP is encouraged by allowing sources to

claim credit for recovery of 100 percent of non-HAP volatile matter

(including water) used in the calculation of equivalent overall organic

HAP control efficiency.

Within the product and package rotogravure and wide-web

flexographic segments, use of non-HAP materials is encouraged by

expressing the overall organic HAP limitation in terms of kg of organic

HAP emitted per kg of solids applied. Use of low HAP materials

decreases the required overall control efficiency. If materials

averaging less than 0.20 kg organic HAP per kg solids applied are used,

no control device is required. This provision makes the use of

waterborne materials without control devices feasible for most

applications.

L. Solicitation of Comments

The Administrator welcomes comments from interested persons on any

aspect of the proposed standards, and on any statement in the preamble

or the referenced supporting documents. In particular, the

Administrator solicits comments on (1) The suitability of EPA Method

311 for determination of HAP in ink and other printing materials; (2)

the mechanism by which owners or operators may accept case-by-case

operating restrictions that would ensure that the potential to emit of

their facility does not exceed the major source threshold; and (3) the

effect of this regulation on effluent from industrial laundries.

The EPA Method 311 was proposed as part of the NESHAP for Wood

Furniture Manufacturing Operations on December 6, 1994 (59 FR 62652).

The comment period for the Wood Furniture NESHAP and Method 311 was

scheduled to close on February 21, 1995. On February 22, 1995 (60 FR

35), the comment period for the proposed Wood Furniture NESHAP was

extended to March 23, 1995 and the comment period for the proposed

Method 311 was extended to April 24, 1995. Persons who submit comments

on the suitability of Method 311 for determination of HAP in ink and

other printing materials in response to the proposed Printing and

Publishing Industry NESHAP should consider also submitting comments in

response to the proposed Method 311. For information on the address and

docket number for submitting comments on the proposed Method 311, see

the February 22, 1995 Federal Register notice.

The proposed standards were developed on the basis of information

available. The Administrator is specifically requesting factual

information that may support either the approach taken in the proposed

standards or an alternate approach. To receive proper consideration,

documentation or data should be provided.

VI. Administrative Requirements

A. Public Hearing

A public hearing will be held, if requested, to discuss the

proposed standards in accordance with section 307(d)(5) of the Act.

Persons wishing to make an oral presentation on the proposed standards

for printing and publishing should contact the EPA at the address given

in the ADDRESSES section of this preamble. Oral presentations will be

limited to 15 minutes each. Any member of the public may file a written

statement before, during, or within 30 days after the hearing. Written

statements should be addressed to the Air and Radiation Docket address

given in the ADDRESSES section of this preamble, and should refer to

Docket No. A-92-42.

A verbatim transcript of the hearing and any written statements

will be available for public inspection and copying during normal

working hours at the EPA's Air and Radiation Docket in Washington, D.C.

(see ADDRESSES section of this preamble).

B. Docket

The docket is an organized and complete file of all the information

submitted to or otherwise considered by the EPA in the development of

this proposed rulemaking. The principal purposes of the docket are: (1)

To allow interested parties to readily identify and locate documents so

that they can intelligently and effectively participate in the

rulemaking process; and (2) to serve as the record in case of judicial

review (except for interagency review materials) (section 307(d)(7)(A)

of the Act).

C. Executive Order 12866

Under Executive Order 12866, (58 FR 51735 (October 4, 1993)) the

Agency must determine whether the regulatory action is ``significant''

and therefore subject to OMB review and the requirements of the

Executive Order. 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 the Executive Order, OMB has notified EPA

that it considers this a ``significant regulatory action'' within the

meaning of the Executive Order. EPA has submitted this action to OMB

for review. Changes made in response to OMB suggestions or

recommendations will be documented in the public record.

[[Page 13683]]

D. Enhancing the Intergovernmental Partnership under Executive Order

12875

In compliance with Executive Order 12875 we have involved state,

local, and tribal governments in the development of this rule. State

and local air pollution control associations participated in work group

meetings and made comments which were incorporated in the proposed

rule.

E. Paperwork Reduction Act

The information collection requirements in this proposed rule have

been submitted for approval to OMB under the Paperwork Reduction Act,

44 U.S.C. 3501 et seq. An Information Collection Request (ICR) document

has been prepared by the EPA (ICR No. 1739.01) and a copy may be

obtained from Sandy Farmer, Information Policy Branch, EPA, 401 M

Street SW., (2136), Washington, DC 20460 or by calling (202) 260-2740.

The public reporting burden for this collection of information is

estimated to average 251 hours per respondent for the first year after

the date of promulgation of the rule, including time for reviewing

instructions, searching existing data sources, gathering and

maintaining the data needed, and completing and reviewing the

collection of information.

Send comments regarding the burden estimate or any other aspect of

this collection of information, including suggestions for reducing this

burden, to Chief, Information Policy Branch, 2136, U.S. Environmental

Protection Agency, 401 M Street SW., Washington, DC 20460; and to the

Office of Management and Budget, Washington, DC 20503, marked

``Attention: Desk Officer for the EPA.'' The final rule will respond to

any OMB or public comments on the information collection requirements

contained in this proposal.

F. Regulatory Flexibility Act

The Regulatory Flexibility Act (or RFA, Public Law 96-354,

September 19, 1980) requires Federal agencies to give special

consideration to the impact of regulation on small businesses. The RFA

specifies that a final regulatory flexibility analysis must be prepared

if a proposed regulation will have a significant economic impact on a

substantial number of small entities. To determine whether a final RFA

is required, a screening analysis, otherwise known as an initial RFA,

is necessary.

Regulatory impacts are considered significant if:

(1) Annual compliance costs increase total costs of production by

more than 5 percent, or

(2) Annual compliance costs as a percent of sales are at least 20

percent higher for small entities, or

(3) Capital cost of compliance represent a significant portion of

capital available to small entities, or

(4) The requirements of the regulation are likely to result in

closures of small entities.

A ``substantial number'' of small entities is generally considered

to be more than 20 percent of the small entities in the affected

industry.

In addition to the requirement above, the Agency requires a final

RFA if any small business impacts are attributed to a regulatory action

for any action initiated after April 1992. In this case, the regulatory

action began before April 1992, so the former RFA requirements are

pertinent.

Consistent with Small Business Administration (SBA) size standards,

a firm is classified as a small entity if it has less than 500

employees for most of the affected industries at the 4-digit SIC code

level, 750 for 3 affected industries at that level (2656--sanitary food

containers, 2657--folding paperboard boxes, and 3221--glass

containers), and 1,000 for 1 affected industry (3411--metal cans); and

is unaffiliated with a larger entity.

Using the information above, none of the firms in the publication

gravure sector are small. For the packaging and product gravure sector,

29 out of 60 firms, or 48.3 percent are classified as small. For the

flexographic sector, virtually all of the affected firms are small.

Data were available to examine all four of the criteria.

For the first criterion, the maximum increase in the total cost of

production from compliance with the standard is, on average, 1.4

percent for affected small entities. This is not a significant

increase. For the second, annual compliance costs as a percentage of

sales were calculated to be 9 percent higher for small entities, and

this is not significant. For the third criterion, the increase in costs

from compliance as a percentage of assets and as a percentage of equity

was negligible (less than 1 percent). For the fourth and final

criterion, no small firms are at risk of closure due to the standard.

In conclusion, and pursuant to section 605(b) of the Regulatory

Flexibility Act, 5 U.S.C. 605(b), the Administrator certifies that this

rule will not have a significant economic impact on a substantial

number of small entities. The basis for the certification is that the

economic impacts for small entities do not meet or exceed the criteria

in the Guidelines to the Regulatory Flexibility Act of 1980, as shown

above. Further information on the initial RFA is available in the

background information document.

G. Clean Air Act Section 117

In accordance with section 117 of the Act, publication of this

proposal was preceded by consultation with appropriate advisory

committees, independent experts, and Federal departments and agencies.

The Administrator welcomes comment on all aspects of the proposed

regulation, including health, economic, technological, or other

aspects.

H. Regulatory Review

In accordance with sections 112(d)(6) and 112(f)(2) of the Act,

this regulation will be reviewed within 8 years from the date of

promulgation. This review may include an assessment of such factors as

evaluation of the residual health risk, any overlap with other

programs, the existence of alternative methods, enforceability,

improvements in emission control technology and health data, and the

recordkeeping and reporting requirements.

VII. Statutory Authority

The statutory authority for this proposal is provided by sections

101, 112, 114, 116, and 301 of the Clean Air Act, as amended; 42

U.S.C., 7401, 7412, 7414, 7416, and 7601.

List of Subjects in 40 CFR Part 63

Environmental protection, Air pollution control, Hazardous

substances, Reporting and recordkeeping requirements, Standard for

printing and publishing industry.

Dated: March 1, 1995.

Carol M. Browner,

Administrator.

[FR Doc. 95-5983 Filed 3-13-95; 8:45 am]

BILLING CODE 6560-50-P

This is a copy of a public record, reproduced as it was published. It is not legal advice, and it may not be the version a court would rely on. Check the official source before you cite it.

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National Emission Standards for Hazardous Air Pollutants; Proposed Standards for Hazardous Air Pollutant Emissions From the Printing and Publishing Industry · 60 FR 13664 | Frix