June 1, 2007

rev

Guidance for Setting Reasonable Progress

Goals Under the Regional Haze Program

U.S. Environmental Protection Agency

Office of Air Quality Planning and Standards

Air Quality Policy Division

Geographic Strategies Group

Research Triangle Park, NC
Guidance for Setting Reasonable Progress Goals Under the Regional Haze Program

i

TABLE OF CONTENTS

Abbreviations and Acronyms .................................................. iii

1.0 INTRODUCTION ...................................................... 1 - 1

1.1 Legislative and Regulatory History ............................... 1 - 1

1.2 Meaning of the Term “Reasonable Progress Goal” .................. 1 - 2

1.3 Relationship of Reasonable Progress to BART and 

the Long Term Strategy ........................................ 1 - 4

2.0 OVERVIEW OF THE PROCESS FOR DEVELOPING THE RPG ................... 2 - 1

2.1 Establish Baseline and Natural Visibility Conditions ................ 2 - 1

2.2 Determine the Glidepath, or Uniform Rate of Progress ............... 2 - 2

2.3 Identify and Analyze the Measures Aimed at Achieving

the Uniform Rate of Progress .................................... 2 - 3

2.4 Establish a RPG ............................................... 2 - 4

3.0 IDENTIFYING KEY POLLUTANTS AND SOURCE CATEGORIES FOR THE FIRST PLANNING

PERIOD ............................................................. 3 - 1

3.1 Identification of Source Categories From Which These Pollutants 

and Their Precursors Are Emitted ................................ 3 - 1

4.0 IDENTIFY CONTROL MEASURES FOR CONTRIBUTING SOURCE CATEGORIES FOR THE

FIRST PLANNING PERIOD .............................................. 4 - 1

4.1 Consideration of Emissions Reductions from State, Federal, 

and Local Control Measures ..................................... 4 - 1
Guidance for Setting Reasonable Progress Goals Under the Regional Haze Program

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4.2 Identification of Additional Emission Control Strategies for the 

Source Categories Identified ..................................... 4 - 2

5.0 APPLYING STATUTORY FACTORS TO POTENTIALLY AFFECTED STATIONARY 

SOURCES ........................................................... 5 - 1

5.1 Reasonable Progress Statutory Factor (a): Costs of Compliance ....... 5 - 1

5.2 Reasonable Progress Statutory Factor (b): Time Necessary for Compliance

............................................................. 5 - 2

5.3 Reasonable Progress Statutory Factor (c): Energy and Non-Air Impacts 5 - 2

5.4 Reasonable Progress Statutory Factor (d): The Remaining Useful Life of the

Source ....................................................... 5 - 3
Guidance for Setting Reasonable Progress Goals Under the Regional Haze Program

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Abbreviations and Acronyms

BACT - Best Available Control Technology

BART - Best Available Retrofit Technology

CAA - Clean Air Act

CAIR - Clean Air Interstate Rule 

CFR - Code of Federal Regulations

dv - Deciviews

EPA - Environmental Protection Agency

FLM - Federal Land Manager

FR - Federal Register

NOx - A mixture of nitrogen dioxide (NO2), nitric oxide (NO), and other nitrogen oxide gases

NAAQS - National Ambient Air Quality Standard

OAQPS - Office of Air Quality Planning and Standards

PM2.5 - Particulate Matter of 2.5 microns or less in size

RHR - Regional Haze Rule

RPG - Reasonable Progress Goal

RPO - Regional Planning Organization

SIP - State Implementation Plan

yr - Year
Guidance for Setting Reasonable Progress Goals Under the Regional Haze Program

1

 CAA §169A(b)(2).

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1.0 INTRODUCTION

The purpose of this document is to provide guidance to States in setting reasonable

progress goals (RPGs) as part of their regional haze state implementation plans (SIPs) and in

deciding those measures necessary to meet these goals. We emphasize that this document is

merely guidance and that States or the Environmental Protection Agency (EPA) may elect to

follow or deviate from this guidance, as appropriate. The ultimate determination of whether a

given SIP submission by a State meets the statutory requirements of sections 169A and 169B of

the Clean Air Act (CAA) and the regional haze regulations at 40 CFR 51.300 - 309 will be

accomplished through notice and comment rulemaking in which the facts and circumstances of

each State submission will be evaluated by EPA. 

Under the Tribal Authority Rule, 40 CFR part 49, Tribes have the authority to seek

“treatment as a State” for purposes of administering certain CAA programs, including the

regional haze program. Whether Tribes seek this authority or not, EPA encourages Tribes to

participate in the regional planning efforts to address visibility and to consult with neighboring

States as they develop their regional haze SIPs. We hope that this guidance will provide Tribes

with an understanding of the process for establishing RPGs that will assist them in the

consultation process.

1.1 Legislative and Regulatory History

The CAA was amended in August 1977, and a new section 169A was added for the

protection of visibility in mandatory class I Federal areas (Class I areas) of great scenic

importance. In section 169A(a)(1), Congress established the national goal for visibility

protection: 

Congress hereby declares as a national goal the prevention of any future, and the

remedying of any existing, impairment of visibility in mandatory class I Federal

areas which impairment results from manmade air pollution.

Section 169A(a)(4), in part, requires EPA to “promulgate regulations to assure reasonable

progress toward meeting the national goal.” The CAA also requires States to submit SIPs

containing such emission limits, schedules of compliance, and other measures as may be

necessary to make reasonable progress toward meeting the goal.1
Guidance for Setting Reasonable Progress Goals Under the Regional Haze Program

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 64 FR 35714 (codified at 40 CFR 51.300-309). 

3

 40 CFR 51.308(d)(1). 

4

 40 CFR 51.308(d)(3). 

5

 40 CFR 51.308(e). 

6

 70 FR 39104 (July 6, 2005). 

7

 40 CFR 51.308(d)(1). 

1 - 2

In the CAA Amendments of 1990, Congress added section 169B to strengthen and

reaffirm the national goal. Section169B(e) calls for EPA to “carry out the Administrator's

regulatory responsibilities under [section 169A], including criteria for measuring ‘reasonable

progress’ toward the national goal.”

In response to these mandates, EPA promulgated the regional haze rule (RHR) on July 1,

1999.2 Under section 51.308(d)(1) of this rule, States must “establish goals (expressed in

deciviews) that provide for reasonable progress towards achieving natural visibility conditions”

for each Class I area within a State. These RPGs must provide for an improvement in visibility

for the most impaired days over the period of the implementation plan and ensure no degradation

in visibility for the least impaired days over the same period.3

The RHR also requires States to submit a long-term strategy that includes such measures

as are necessary to achieve the RPG for each Class I area.4

 The regulations require States to

consider major and minor stationary sources, mobile sources, and area sources in developing

their long-term strategies. In addition, States must submit a SIP that contains either emission

limitations representing best available retrofit technology (BART) for certain sources put into

operation between 1962 and 1977 or alternative measures that provide for greater reasonable

progress than BART.5

 The BART requirements were addressed in a rule revising certain

provisions of the regulations in section 51.308(e) and promulgating the BART Guidelines.6

1.2 Meaning of the Term “Reasonable Progress Goal”

 States must establish RPGs, measured in deciviews (dv), for each Class I area for the

purpose of improving visibility on the haziest days and ensuring no degradation in visibility on

the clearest days over the period of each implementation plan.7 RPGs are interim goals that

represent incremental visibility improvement over time toward the goal of natural background

conditions and are developed in consultation with other affected States and Federal Land
Guidance for Setting Reasonable Progress Goals Under the Regional Haze Program

8

 40 CFR 51.308(d)(1)(iv) and 51.308(i).

9

 CAA §169A(g)(1); 40 CFR 51.308(d)(1)(i)(A). 

10 40 CFR 51.308(d)(1)(i)(B).

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Managers (FLM).8

In determining what would constitute reasonable progress, section 169A(g) of the CAA 

requires States to consider the following four factors:

• The costs of compliance;

• The time necessary for compliance;

• The energy and non-air quality environmental impacts of compliance; and

• The remaining useful life of existing sources that contribute to visibility impairment.9

States must demonstrate in their SIPs how these factors are taken into consideration in selecting

the RPG for each Class I area in the State.

The discussion of the statutory factors in this guidance is largely aimed at helping States

apply these factors in considering measures for point sources. States may find that the factors

can be applied to sources other than point sources; the meaning of the factors, however, should

not be unduly strained in order to fit non-point sources. In other words, if common sense dictates

that a particular statutory factor cannot be applied to a particular source category, then the State’s

analysis may reflect that fact, and emissions reductions from such sources may still be included

in the SIP.

As noted above, the RHR establishes an additional analytical requirement for States in the

process of establishing the RPG. This analytical requirement requires States to determine the

rate of improvement in visibility needed to reach natural conditions by 2064, and to set each RPG

taking this “glidepath” into account.10 (The process for determining the glidepath is discussed

later in this document.) EPA adopted this approach, in part, to ensure that States use a common

analytical framework that accounts for the regional differences affecting visibility and, in part, to

ensure an informed and equitable decision making process. The glidepath is not a presumptive

target, and States may establish a RPG that provides for greater, lesser, or equivalent visibility

improvement as that described by the glidepath.
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 40 CFR 51.308(d)(3), 

1 - 4

In deciding what amount of emissions reduction is appropriate in setting the RPG, you

should take into account the fact that the long-term goal of no manmade impairment

encompasses several planning periods. It is reasonable for you to defer reductions to later

planning periods in order to maintain a consistent glidepath toward the long-term goal.

1.3 Relationship of Reasonable Progress to BART and the Long-Term Strategy

The RPGs, the long-term strategy, and BART (or alternative measures in lieu of BART)

are the three main elements of the regional haze SIPs that States are required to submit by

December 17, 2007. The long-term strategy and BART emissions limitations or other alternative

measures, including cap-and-trade programs or other economic incentive approaches, are

inherently related to the RPG. The long-term strategy is the compilation of “enforceable

emissions limitations, compliance schedules, and other measures as necessary to achieve the

[RPGs],”11 and is the means through which the State ensures that its RPG will be met. BART

emissions limits (or alternative measures in lieu of BART, such as the Clean Air Interstate Rule

(CAIR)) are one set of measures that must be included in the SIP to ensure that an area makes

reasonable progress toward the national goal, and the visibility improvement resulting from

BART (or a BART alternative) is included in the development of the RPG.
Guidance for Setting Reasonable Progress Goals Under the Regional Haze Program

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 64 FR at 35730. 

13

 For more detail on determining baseline and natural conditions, you can review the preamble and

regulations in the RHR, 64 FR at 35728 – 35730, 40 CFR 51.308(d)(2), EPA’s Guidance for Tracking Progress

Under the Regional Haze Rule, EPA-454/B-03-004 (September 2003) available at

www.epa.gov/ttn/oarpg/t1/memoranda/rh_tpurhr_gd.pdf, and EPA’s Guidance for Estimating Natural Visibility

Conditions Under the Regional Haze Rule, EPA-454/B-03-005 (September 2003) available at

www.epa.gov/ttn/oarpg/t1/memoranda/rh_envcurhr_gd.pdf.

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2.0 OVERVIEW OF THE PROCESS FOR DEVELOPING THE RPG

Development of the RPG for each Class I area should be a collaborative process among

State, local, and Tribal authorities, Regional Planning Organizations (RPOs), and FLMs. Steps

for developing RPGs will be briefly outlined in this section of the guidance, along with

references to other guidance and rules where additional detail can be found. The remaining

sections of this guidance expand on particular aspects of these steps. In addition, as this is

guidance for States in developing RPGs, the use of “you” through the rest of the document refers

to States.

2.1 Establish Baseline and Natural Visibility Conditions

To track progress toward the national goal, the RHR, among other things, requires you to

establish the “baseline conditions” representing visibility for the best and worst days at the time

the regional haze program is established for each Class I area. Once established, the baseline

represents the starting point from which reasonable progress will be measured. The RHR also

requires you to estimate “natural conditions” for each Class I area that represents the visiblity

conditions that would exist in the absence of man-made impairment.

As explained in the RHR, the baseline for each Class I area is the average visibility (in

dv) for the 20 percent most impaired days, or “worst days”, and for the 20 percent least impaired

days, or “best days,” for the years 2000 through 2004.12 Using available monitoring data for the

2000 to 2004 time period, you are required to calculate the baseline by averaging the annual

values (in dv) for the 20 percent worst days in each year (yr) to produce a single value (in dv) that

represents the baseline conditions for the worst days. You should follow the same approach for

determining the value that represents the baseline conditions for the best days. Natural

conditions at each Class I area are also expressed by reference to the level of visibility (in dv) for

the 20 percent most impaired and least impaired days.13
Guidance for Setting Reasonable Progress Goals Under the Regional Haze Program

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Figure 1

2.2 Determine the Glidepath, or Uniform Rate of Progress

By comparing baseline conditions with natural conditions, you can determine the uniform

rate of visibility improvement, or progress, needed to reach natural conditions by 2064 for each

Class I area. Figure 1, below, illustrates the basic steps in the process for calculating the uniform

rate of progress toward natural conditions for the first planning period at a hypothetical Class I

area. 

Figure 1 Example of a Uniform Rate of Progress

• Compare baseline conditions to natural conditions. The difference between these two

represents the amount of progress needed to reach natural visibility conditions. In this

example, the State has determined that the baseline for the 20 percent worst days for the

Class I area is 29 dv and estimated that natural background is 11 dv, a difference of 18

dv.

• Calculate the annual average visibility improvement needed to reach natural conditions

by 2064 by dividing the total amount of improvement needed by 60 years (the period

between 2004 and 2064). In this example, this value is 0.3 dv/yr.
Guidance for Setting Reasonable Progress Goals Under the Regional Haze Program

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• Multiply the annual average visibility improvement needed by the number of years in the

first planning period (the period from 2004 until 2018). In this example, this value is 4.2

dv. This is the uniform rate of progress that would be needed during the first planning

period to attain natural visibility conditions by 2064.

If you were to achieve this steady improvement in visibility over the next 60 years, you would

reach the national goal by 2064.

2.3 Identify and Analyze the Measures Aimed at Achieving the Uniform Rate of

Progress. 

The next step in setting an RPG is to identify and analyze the measures aimed at

achieving the uniform rate of progress and to determine whether these measures are reasonable

based on the statutory factors identified in Section 1.2 above. To meet this requirement, we

suggest the following approach which ensures that States consider all reasonable measures in

developing their regional haze SIPs:

• Identify the key pollutants and sources and/or source categories that are contributing to

visibility impairment at each Class I area. The sources of impairment for the most

impaired and least impaired days may differ. Section 3 discusses this process.

• Identify the control measures and associated emission reductions that are expected to

result from compliance with existing rules and other available measures for the sources

and source categories that contribute significantly to visibility impairment. This is

covered in more detail in Section 4.

• Determine what additional control measures would be reasonable based on the statutory

factors and other relevant factors for the sources and/or source categories you have

identified. 

• Estimate through the use of air quality models the improvement in visibility that would

result from implementation of the control measures you have found to be reasonable and

compare this to the uniform rate of progress.

Another possible approach that some States and RPOs are using is to “back out” the

measures necessary to achieve the uniform rate of progress. In this process, States are using

dispersion modeling to estimate the visibility impacts of a specific percentage reduction in

visibility impairing pollutants. The resulting visibility conditions are then compared to the

uniform rate of progress. Using this process, States will be able to identify a percentage
Guidance for Setting Reasonable Progress Goals Under the Regional Haze Program

14 40 CFR 51.308(d)(1)(iv).

15 40 CFR 51.308(d)(1)(i)(A).

2 - 4

reduction in visibility impairing pollutants that would provide progress at or beyond the uniform

rate of progress. In a separate step, States would consider the statutory factors along with other

relevant factors to select appropriate measures to achieve the identified reduction in emissions. 

States can thus identify the measures that would be needed to achieve the uniform rate of

progress at a Class I area and determine whether such measures are reasonable. 

2.4 Establish a RPG

In developing a RPG, you must consult with other States with emissions sources that may

reasonably be anticipated to cause or contribute to visibility impairment at Class I areas in your

State.14 The regulations anticipate that States may not always agree on what measures would be

reasonable or on the appropriateness of a RPG. We encourage States to work together early and

often to resolve such issues. In addition, the FLMs may provide insight and assistance to States

in identifying regional approaches to address the RPG.

The improvement in visibility resulting from implementation of the measures you have

found to be reasonable, considering the uniform rate of progress, is the amount of progress that

represents your RPG. The regional haze rule requires you to clearly support your RPG

determination in your SIP submission based on the statutory factors. 15
Guidance for Setting Reasonable Progress Goals Under the Regional Haze Program

16

 40 CFR 51.308(d)(3)(iv).

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3.0 IDENTIFYING KEY POLLUTANTS AND SOURCE CATEGORIES FOR THE FIRST PLANNING

PERIOD

This process begins with the identification of key pollutants and source categories that

contribute to visibility impairment at the Class I area. Such analysis has been the subject of

considerable study over the past decade, including studies by the Grand Canyon Visibility

Transport Commission and ongoing work by RPOs. For the purpose of this document, it is

assumed that analyses identifying the key pollutants contributing to visibility impairment have

been conducted for each Class I area.

3.1 Identification of Source Categories From Which These Pollutants and Their

Precursors Are Emitted

Once the key pollutants contributing to visibility impairment at each Class I area have

been identified, the sources or source categories responsible for emitting these pollutants or

pollutant precursors can also be determined. There are several tools and techniques being

employed by the RPOs to do so, including analysis of emission inventories, source

apportionment, trajectory analysis, and atmospheric modeling. Technical guidance on these tools

and techniques is beyond the scope of this document. Instead, this document focuses on policy

considerations relevant to the identification of which source categories should be considered as

part of the regional haze SIP development process. 

When identifying the sources or source categories responsible for regional haze, you

should consider the relationship between the RPG and the requirements for long-term strategies. 

The regulations require States to consider major and minor stationary sources, as well as mobile

and area sources, in developing long-term strategies.16 At a minimum, the regulations require

you to consider several factors when developing a long-term strategy, including the following:

• Emissions reductions due to ongoing air pollution control programs, including

measures to address reasonably attributable visibility impairment and those taken

to attain the fine particulate matter (PM2.5) national ambient air quality standards

(NAAQS).

• Measures to mitigate the impact of construction activities.

• Smoke management techniques for agricultural and forestry management

purposes.
Guidance for Setting Reasonable Progress Goals Under the Regional Haze Program

17

 40 CFR 51.308(d)(3)(v).

3 - 2

• Anticipated visibility effects from changes in point, area, and mobile source

emissions.17

As illustrated by these factors, States should consider a broad array of sources and

activities when deciding which sources or source categories contribute significantly to visibility

impairment.
Guidance for Setting Reasonable Progress Goals Under the Regional Haze Program

18 40 CFR 51.308(d)(1)(vi). 

19

 40 CFR 51.308(d)(3)(iii) provides that the baseline emission inventory year is presumed to be the most

recent year of the consolidated emissions inventory for the SIP. A memorandum from OAQPS, entitled 2002 Base

Year Emission Inventory SIP Planning: 8-hr Ozone, PM 2.5, and Regional Haze Programs (November 18, 2002)

(“2002 EI Memo”), identifies 2002 as the anticipated baseline emission inventory year for regional haze. 

 See www.epa.gov/ttn/oarpg/t1/memoranda/2002bye_gm.pdf

20

 2002 EI Memo at 3-4.

4 - 1

4.0 IDENTIFY CONTROL MEASURES FOR CONTRIBUTING SOURCE CATEGORIES FOR THE

FIRST PLANNING PERIOD

There are numerous possible conceptual approaches that you can use to identify control

measures for the long-term strategy and the related RPG. We suggest beginning by concentrating

on possible emissions reductions of several pollutant species from a few selected source sectors,

focusing on those source categories that may have the greatest impact on visibility at Class I

areas, considering cost and the other factors discussed further in Section 5.0. 

4.1 Consideration of Emissions Reductions from State, Federal, and Local Control

Measures

One important factor to keep in mind when establishing a RPG is that you cannot adopt a

RPG that represents less visibility improvement than is expected to result from the

implementation of other CAA requirements.18 You must therefore determine the amount of

emission reductions that can be expected from identified sources or source categories as a result

of requirements at the local, State, and federal levels during the planning period of the SIP and

the resulting improvements in visibility at Class I areas. Given the significant emissions

reductions that we anticipate to result from BART, the CAIR, and the implementation of other

CAA programs, including the ozone and PM2.5 NAAQS, for many States this will be an

important step in determining your RPG, and it may be all that is necessary to achieve reasonable

progress in the first planning period for some States. 

The first step in this process is to identify the baseline emissions inventory year on which

your strategies are based. For the first RHR SIP, we anticipate that States will use 2002 as the

baseline year for emission inventories.19 If you do use 2002, you may take credit in your longterm strategy for emission reductions achieved after 2002. This includes emission reductions

from measures implemented to attain the ozone and PM2.5 NAAQS,20 and Federal programs, such

as the national mobile source program and federal standards for hazardous air pollutants (air

toxics).
Guidance for Setting Reasonable Progress Goals Under the Regional Haze Program

21 Information on AirControlNETcan be found at www.epa.gov/ttn/ecas/econtool.html. The

RACT/BACT/LAER Clearinghouse is located at http://cfpub.epa.gov/rblc/htm/bl02.cfm.

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4.2 Identification of Additional Emissions Control Strategies for the Source Categories

Identified

After determining the amount of emissions reductions of visibility impairing pollutants

that may be expected from implementation of other CAA programs, you will be ready to identify

any additional measures that are reasonable. The RHR gives States wide latitude to determine

additional control requirements, and there are many ways to approach identifying additional

reasonable measures; however, you must at a minimum, consider the four statutory factors. 

Based on the contribution from certain source categories and the magnitude of their emissions

you may determine that little additional analysis is required to determine further controls are not

warranted for that category. As discussed further in section 5, you have considerable flexibility

in how you take these factors into consideration. In addition to source-specific controls,

emissions cap-and-trade programs may be considered. Sources of information on control

techniques for specific source categories include the RACT/BACT/LAER Clearinghouse and

EPA’s AIRControlNet database.21

One approach that you could take to streamline what could be an extremely complex task

would be to first identify alternative control scenarios with different levels of stringency. Each

control scenario would assume application of specific control levels or measures to the sources or

source categories you have identified as the significant sources of visibility impairment. As

indicated previously in section 4.1, the starting point for this assessment is the visibility

improvement achieved as a result of BART, the CAIR, and the implementation of other CAA

programs, including other measures for attainment of the ozone and PM2.5 NAAQS. You would

then consider whether any additional control scenarios are reasonable based on your

consideration of the statutory factors and any other factors you have determined are relevant.

Another approach you could take, consistent with the “back out” approach discussed in

section 2.3, would involve identifying the set of emissions control measures that achieves the

target percentage reductions in visibility-impairing pollutants associated with progress at or

beyond the uniform rate of progress. The selection of control measures to include in this set

would be guided by your consideration of the statutory factors and any other factors you have

determined are relevant.

Note that for some sources determined to be subject to BART, the State will already have

completed a BART analysis. Since the BART analysis is based, in part, on an assessment of

many of the same factors that must be addressed in establishing the RPG, it is reasonable to
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conclude that any control requirements imposed in the BART determination also satisfy the

RPG-related requirements for source review in the first RPG planning period. Hence, you may

conclude that no additional emissions controls are necessary for these sources in the first

planning period.
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 As noted above, application of the cost factor to non-point sources is beyond the scope of this guidance. 

This is also true for mobile sources.

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5.0 APPLYING STATUTORY FACTORS TO POTENTIALLY AFFECTED STATIONARY SOURCES

In determining reasonable progress, CAA §169A(g)(1) requires States to take into

consideration a number of factors. However, you have flexibility in how to take into

consideration these statutory factors and any other factors that you have determined to be

relevant. For example, the factors could be used to select which sources or activities should or

should not be regulated, or they could be used to determine the level or stringency of control, if

any, for selected sources or activities, or some combination of both. The factors may be

considered both individually and/or in combination. As noted in section 4.1, given the

significant emissions reductions that we anticipate to result from BART, the CAIR, and the

implementation of other CAA programs, these reductions may be all that is necessary to achieve

reasonable progress in the first planning period for some States. Also, as noted in section 4.2, it

is not necessary for you to reassess the reasonable progress factors for sources subject to BART

for which you have already completed a BART analysis.

5.1 Reasonable Progress Statutory Factor (a): Costs of Compliance

The first factor to take into consideration is the “costs of compliance.” In this context we

believe that the cost of compliance factor can be interpreted to encompass the cost of compliance

for individual sources or source categories, and more broadly the implication of compliance costs

to the health and vitality of industries within a state. For additional guidance on applying the cost

of compliance factor to stationary sources, you may wish to consult the BART guidelines,

referenced above. 

To assess compliance costs for individual sources or source categories potentially subject

to emission limitations, we suggest that you use established control cost analysis techniques. For

stationary sources, generally this involves the following:22

a) Identify the emissions units to be controlled;

b) Identify the design parameters for emissions controls; and

c) Develop cost estimates based upon those design parameters.
Guidance for Setting Reasonable Progress Goals Under the Regional Haze Program

23 Any additional information used for the cost calculations, including any information supplied by vendors

that affects your assumptions regarding purchased equipment costs, equipment life, replacement of major

components, and any other element of the calculation that differs from the Control Cost Manual, should be

documented. EPA’s Control Cost Manual is located at: www.epa.gov/ttncatc1/products.html#cccinfo.

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You should evaluate both average and incremental costs. To maintain and improve consistency

wherever possible, cost estimates should be based on EPA’s Air Pollution Control Cost

Manual.

23

 

 In considering the cost of compliance factor, you should keep in mind that different

pollutants differently impact visibility impairment. For example, on a ton basis, sulfur dioxiderelated particles have a greater impact on visibility impairment than crustal material. Therefore,

in assessing additional emissions reduction strategies for source categories or individual, large

scale sources, simple cost effectiveness estimates based on a dollar-per-ton calculation may not

be as meaningful as a dollar-per-deciview calculation, especially if the strategies reduce different

groups of pollutants.

5.2 Reasonable Progress Statutory Factor (b): Time Necessary for Compliance

The second factor is the “time necessary for compliance.” It may be appropriate for you

to use this factor to adjust the RPG to reflect the degree of improvement in visibility achievable

within the period of the first SIP if the time needed for full implementation of a control measure

(or measures) will extend beyond 2018. For example, if you anticipate that constraints on the

availability of construction labor will preclude the installation of controls at all sources of a

particular category by 2018, the visibility improvement anticipated from installation of controls

at the percentage of sources that could be controlled within the strategy period should be

considered in setting the RPG and in establishing the SIP requirements to meet the RPG.

5.3 Reasonable Progress Statutory Factor (c): Energy and Non-Air Impacts

The third factor is “energy and non-air environmental impacts.” In assessing energy

impacts, you may want to consider whether the energy requirements associated with a control

technology result in energy penalties. For example, controls on diesel engines may decrease the

engine’s fuel efficiency, leading to an increase in diesel fuel consumption. Or, a particular

control may require a fuel unavailable in the area. To the extent that these considerations are

quantifiable they should be included in the engineering analyses supporting compliance cost

estimates.

Some examples of non-air environmental impacts that you may wish to consider, are the

effects of the waste stream that may be generated by a particular control technology, and/or other
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resource consumption rates such as water, water supply, and waste water disposal. To the extent

that these considerations are quantifiable, they should also be included in the analyses supporting

compliance cost estimates.

For additional guidance on applying this factor to stationary sources, you may wish to

consult the BART Guidelines, referenced above.

5.4 Reasonable Progress Statutory Factor (d): The Remaining Useful Life of the Source

The fourth statutory factor is “the remaining useful life of any existing source subject to

[reasonable progress] requirements.” This factor is generally best treated as one element of the

overall cost analysis. The “remaining useful life” of a source, if it represents a relatively short

time period, may affect the annualized costs of retrofit controls. For example, the methods for

calculating annualized costs in EPA’s Air Pollution Control Cost Manual require the use of a

specified time period for amortization that varies based upon the type of control. If the

remaining useful life of the source will clearly exceed this time period, the remaining useful life

factor has essentially no effect on control costs and on the reasonable progress determination

process. Where the remaining useful life of the source is less than the time period for amortizing

the costs of the retrofit control, you may wish to use this shorter time period in your cost

calculations.

For additional guidance on applying this factor to stationary sources, you may wish to

consult the BART Guidelines, referenced above.