EPA-450/2-80-083a
   Summary of Comments and  Responses
on the May 22,  1980 Proposed Regulations
           for Visibility Protection for
               Federal Class  I Areas
                            by

                     PEDCo Environmental, Inc.
                        11499 Chester Rd.
                      Cincinnati, Ohio 45246
                      Contract No. 68-02-3512
                         Prepared for

                 U.S. ENVIRONMENTAL PROTECTION AGENCY
                    Office of Air, Noise, and Radiation
                 Office of Air Quality Planning and Standards
                 Research Triangle Park, North Carolina 27711

                         October 1980

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This report is issued by the Environmental Protection Agency to report technical data of
interest to a limited number of readers.  Copies are available - in limited quantities - from
the Library Services  Office (MD-35) , U.S. Environmental Protection Agency, Research
Triangle Park, North Carolina 27711; or, for a fee, from the National Technical Infor-
mation Service, 5285  Port Royal Road, Springfield, Virginia 22161.
                        Publication No. EPA-450/2-80~083a
                                        11

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                            CONTENTS
Tables
1.
Introduction
2.   Identification of Major Issues

     2.1  Definition of visibility impairment
     2.2  Definition of stationary source
     2.3  Responsibilities of FLM
     2.4  Integral vistas
     2.5  Long-term strategies
     2.6  Best available retrofit technology
     2.7  Prescribed burning
     2.8  Phased approach
     2.9' Technical guidance
     2.10 New source review
     2.11 Costs versus::.benefits
     2.12 Identification under Section  169A(a)(2)
          of mandatory Class I Federal  areas in
          which visibility is an important value
     2.13 Miscellaneous

3.   Summary of Comments by  Issue

4.   Response to Major Comments

     4.1  Definition of visibility  impairment
     4.2  Existing stationary facility
     4.3  Responsibilities of the FLM
     4.4  Integral vistas
     4.5  Long term  strategies
     4.6  Best available retrofit  technology
     4.7  Prescribed burning
     4.8  Phased approach
     4.9  Technical  guidance
     4.10 New source review
     4.11 Costs versus benefits
     4.12 Identification under  Section  169A(a)(2)
          of mandatory  Class I  Federal  areas  in
          which visibility  is  an important value
     4.13 Miscellaneous
 Appendix A
           Summary of individual comments
                                                             IV

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                             TABLES
Number

   1


   2
   4

   5

   6

   7

   8

   9

   10

   11

   12


   13
Summary of Comments - Definition of
  Visibility Impairment

Summary of Comments - Definition of
  Stationary Source  .

Summary of Comments - Responsibilities
  of FLM

Summary of Comments - Integral Vistas

Summary of Comments - Long-Term Strategies

Summary of Comments - BART

Summary of Comments - Prescribed Burning

Summary of Comments - Phased Approach

Summary of Comments - Technical Guidance

Summary of Comments - New Source Review

Summary of Comments - Costs vs. Benefit

Summary of Comments - Identification under
  Section 169A(a)(2)

Summary of Comments - Miscellaneous
Page


 15


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 29

 44

 68

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 84

 101

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 119

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 141

 142
                                IV

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                            SECTION 1
                          INTRODUCTION

     The  Environmental  Protection Agency  (EPA) proposed  rule-
making  to  protect visibility  for  Federal  Class  I  areas  on
May 22, 1980 at p. 34762 of the Federal Register.  This proposed
rulemaking  was  required by Section 169A  of the Clean  Air Act
(the Act) with the goal of "...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."
     These regulations (1) require States to consider visibility
protection  for  mandatory Class I  Federal  areas including inte-
gral vistas,  (2)  require  certain  existing stationary facilities
to be  analyzed  for and in some cases to install the Best Avail-
able Retrofit Technology (BART) for controlling those pollutants
which  cause visibility impairment.,  (3) require States to iden-
tify,  evaluate,  and adopt  long-term strategies for making rea-
sonable progress toward remedying existing and preventing future
impairment  in the mandatory Class I Federal areas,  and (4) re-
quire  the  adoption of certain measures that will supplement the
States  new source  review program regarding visibility impact.
     There  were  a  total   of 383  comments  received  from the
public.   There were  also  fourteen  comments  submitted through
Congressional channels; these are  IV-C-3 through IV-C-16 and may
be found in the Docket.  The comments received by way of members
of Congress are summarized in Appendix A.
     As  part of this report, the  comments have been summarized
and  major  issues  by  the commenters  have  been  identified.   A
summary  of responses to the  comments  has  also been included in

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this report.  The  commenters  fell into five major groups:  pri-
vate citizens,  citizen  and environmental  groups;  agricultural
and forestry  organizations; private  industry and industrial as-
sociations; and government agencies or representatives-—Federal,
State,  and local.
     There  were 138  comments  from private  citizens.   The vast
majority  of these comments were  highly supportive of  the pro-
posed  regulations, but  only  a few  commented on  the  specific
details  in  the  proposed  regulations.   Many  of  the  citizens
expressed  support for the  concept of integral vistas.   Some of
the  citizens  commented  on the  lack of  an adequate  monitoring
program, and urged further development in this area.  There were
eight  citizens  which recommended  that the  role  of the Federal
Land Manager  be strengthened  in the  regulations.  Some citizens
opposed the regulation of prescribed  burning.
     There were twenty-two comments from citizen  and environmen-
tal organizations.  Most of these commenters were supportive of
the proposed regulations, and many had substantive comments con-
cerning  particular aspects of  the   proposed  regulations.   The
comments  ranged from the  need for increased monitoring efforts
to  giving the  Federal  Land Manager the principal role  in the
identification  of integral vistas.   The  comments by  this group
were very similar to  those submitted by many private citizens.
     A total of thirty-one  comments were received from foresters
and  agricultural  or  forestry organizations.   Virtually  all of
these  commenters were concerned with  the regulation of prescrib-
ed burning,  and they  were all opposed  to any further require-
ments  to  control burning beyond that which might be now imposed
by a State  agency.
     There  were 134 comments  from private companies  or organi-
zations  representing private  companies.    Of  these,  forty-four
were public utilities.   Most,  but not all  of  the commenters op-
posed  the proposed regulations in general.   The comments from
this group were very diverse and very detailed and they covered
virtually every  aspect of the regulations  from the  definition of
visibility impairment to-the concept  of integral  vistas.
                                2

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     Comments  from  State,  Federal,  and  local governments  or
their agencies totaled fifty-four.  The majority of the comments
from local governments were concerning the impact of the regula-
tions on  the local economy, and  the  commenters felt the effect
would be  negative.   The  comments from State and Federal govern-
ment dealt  with their respective roles  in the proposed regula-
tions.  They also provided a variety of substantive technical
comments.    Almost all  government  commenters,  other  than some
State and local  agencies,  strongly supported these proposed re-
gulations.
     The  involvement of the  FLM in  the visibility regulations
and  the  concept of  "integral  vistas" were by far the two most
frequent  issues  raised  in  comments.  There was also a consider-
able  amount of concern over the  BART requirements and the need
for  more  guidance  and data to implement  the visibility program.

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                            SECTION 2
                 IDENTIFICATION OF MAJOR ISSUES

     Major issues  were identified as  a result of  the  comments
received on the May 22, 1980, Proposed Regulations on Visibility
Protection for  Federal Class  I  areas.   These issues covered  a
variety of topics  and touched on many aspects  of  the  proposed
regulations and supporting material  or guidelines.   The follow-
ing  subsections briefly summarize the major  issues  in  order to
have  a  clear understanding of the basic  concerns raised by the
commenters.  The actual summaries of the comments by major issue
and  subissue  are presented in a series of  tables in Section 3.
This section is intended as a key to explain the headings on the
tables in Section 3.

2.1  DEFINITIONS OF "VISIBILITY IMPAIRMENT"
     Most of  the comments  on definitions dealt with "visibility
impairment"  and related terms.   The majority of these comments
were  negative with respect to certain terms used in the defini-
tion.   The  most frequently  raised issues are listed in Section
3.
2.1.1   "Human Perception"
     Many  comments were concerned with the meaning or applica-
tion  of the  term  "human perception"  of  visibility impairment.
This  term  appears  in the definition of "visibility impairment,"
and  restricts the  perceptibility  to the observation by humans.
Many  of the comments  related  to  the subjectivity of this term.
2.1.2  Any vs. Significant
      Several  of the comments  received stated that, rather than
the  term  "any" in the definition of "visibility impairment," a

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substitution of  "significant"  should be made.   There  were sev-
eral  different types  of  comments  related  to  this  which  are
grouped in the summary.
2.1.3  Definition of "Adverse Impact"
     The  definition of  "adverse  impact"  is closely related to
that  of  "significant impairment," as was noted by several com-
menters.  "Adverse  impact"  also  has  a particular application in
the  regulations  in § 51.307, which made it  the subject of com-
ments .
2.1.4  "Natural Conditions"
     There were  a  significant  number of comments on the defini-
tion of natural conditions.  These comments were summarized, and
in  some cases the commenters  offered  an  alternate definition.

2.2  DEFINITION OF  "STATIONARY SOURCE"
     The  definition of  "stationary  source"  is related  to the
Alabama Power  decision;  this   and  other  relevant points were
raised by the  commenters.
2.2.1  'Regulated vs. Any Pollutant
      Several  comments were  received concerning the  terms  "any
air  pollutant"  in the definition of  stationary source.  There
were also comments as  to  what "regulated" should refer to in
this rulemaking.
2.2.2   "Reconstruction"
      Although  "reconstruction" is a  separate  definition, it is
closely related to  that of stationary source, and refers  to  a
stationary  source.
2.2.3  "Potential  to Emit"
      The  definition of "potential to emit"  also refers to "sta-
tionary source."  Comments  concerning  this  definition were made
 several times  relative to  the  Alabama Power decision.

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2.3  RESPONSIBILITIES OF THE FEDERAL LAND MANAGERS
     Various aspects of  the  role of the Federal Land Manager in
the proposed regulations prompted  a variety of  comments.   The
Federal  Land  Manager   was   identified  as  a  participant  in
§ 51.302, §  51.303,  §  51.304,  § 51.305, §  51,306,  and § 51.307
of the proposed regulations.
2.3.1  Affirmative Responsibilities
     The way in  which the role  of  the  Federal  Land Manager was
perceived  in the  proposed  regulations,  and  that  role as  it
appears  in  Sections  165  and 169A of the Act was  the subject of
numerous comments.  These comments varied from supportive of the
Federal  Land  Manager's  role  in the  proposed  regulations  to
highly critical of that  role.
2.3.2  Approval/Disapproval
     Several  commenters  expressed concern over  the  amount of
decisionmaking  authority given  to the Federal Land Manager in
the proposed regulations.
2.3.3  PSD
     The role of the  Federal Land Manager in  §  51.307 was the
subject  of  some  debate.  The  implementation of that role was
also commented upon.
2.3.4  Invo1vement/Noninvo1vement
     The involvement or  noninvolvement  of the FLM in the various
aspects  of the visibility  regulations  were commented.upon.  In
addition,   the  degree   of   involvement,  e.g.,   SIP  revisions,
§  51.302, was commented upon by  individuals and  representatives
of citizen's  groups, government,  and industry.

2.4  INTEGRAL VISTAS
     Section 51.304  and §  51.307  of  the  proposed regulations
deal with or have portions  dealing with integral  vistas.  Numer-
ous comments were made  concerning this  concept.

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2.4.1  Not Authorized
     One area  of concern for many commenters was  that  the con-
cept of integral vistas  was  not authorized in the Clean Air Act
either explicitly or implicitly.
2.4.2  Better Procedures
     Many commenters felt there were better procedures available
for the identification of  integral  vistas or that better proce-
dures could be  developed.  Comments  were made on the procedures
as they  appeared in the guideline,  "Criteria  for the Identifi-
cation of Integral Vistas" (draft).
2.4.3  Secretary of the Interior vs. State      . .  .-
     The Federal Land Manager (defined in the regulations as the
Secretary) was  given  a  substantial  role in the proposed regula-
tions to identify  and protect integral vistas for Federal Class
I areas.  There were  comments both pro and con on the  level of
involvement in  identifying and protecting integral vistas by the
Federal Land Manager.
2.4.4  Burden on Planning New Sources
     Some  commenters  stated the  various  aspects  of  integral
vistas,  as  proposed  in the  regulations,  would  place  an 'undue
burden on the  planning  and siting of new sources.  A summary of
these comments  is included in Section 3.

2.5  LONG-TERM  STRATEGIES
     Section  51.306 calls for  the  State  to include a long-term
strategy  in their  State  Implementation Plan (SIP) revision for
visibility  and  to  explain how they will  progress towards the
national goal  set by Congress.   Comments were received concern-
ing  the requirements outlined  in  this section of the proposed
regulation.
2.5.1  Existing
     A  variety  of  comments   were  received on  the inclusion of
existing  sources   long-term  strategy.    The  SIP  revision  must
                                 7

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address certain  areas  of the long-term strategy  as  they relate
to other than BART  sources  causing visibility impairment.  Com-
ments were summarized  dealing with this  aspect as identified in
§ 51.302 and § 5i:306.
2.5.2  New Source
     The proposed regulations require the SIP revision  to in-
clude  a plan  for the  long-term strategy  of dealing with new
sources which  may impair visibility  or  impact integral  vistas.
2.5.3  Periodic Review
     The long-term strategy section requires that the plan shall
provide for a periodic review and for revision as appropriate at
least  every three  years.   Comments  were made  concerning what
this review should include and  concerning the frequency of the
review in the proposed regulations.

2.6  BEST AVAILABLE RETROFIT TECHNOLOGY
     The requirement to  apply Best Available Retrofit Technology
 (BART)  to existing  sources is  in  §  51.302.   Numerous comments
were  received on various  aspects  of BART as  presented in the
proposed regulations.
2.6.1   Timing
     There  were  comments  concerning the time period available
 for  the Federal  Land  Manager to identify candidate sources for
BART  analysis.   There  were also comments on the time available
 for an SIP  revision.
2.6.2   Impact  on All Sources
     Most of the comments  on  BART analysis were from industry  or
 industrial  organizations.  There  was concern about the  impact,
 on sources which may  be identified for the purpose of  applying
BART.
                                 8

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2.6.3  Reanalysis
     The Section 51.306(e) requirement in the long-term strategy
to perform  a reanalysis of BART for  a  pollutant  not previously
controlled generated numerous comments.
2.6.4  Cost
     The  cost of  BART  as  applied  to  various   industries  was
commented upon.   These  comments  were  from  industry,  citizens,
and citizen's groups.
2.6.5  FLM Involvement
     The  involvement of  the Federal Land Manager  in  the BART
process  was  commented  upon  by  government  agencies,  States,
citizens, and industry.
2.6.6  State Responsibility
     State  responsibility in the BART  process  was addressed by
several commenters.

2.7  PRESCRIBED BURNING
     The  requirement for  the  long-term strategy  developed by  a
State  to  include  smoke  management  techniques  for prescribed
burning  is  in § 51.306(f)(5).  A very  large number of comments
were received on this  issue.
2.7.1  Not  a Major  Source
     Many commenters  stated that prescribed  burning  is  not  a
major  source.
2.7.2  Preferable to Wildfire
     Most commenters stated that prescribed burning is prefera-
ble  to wildfire.
2.7.3   Forest Management
     The point  was frequently made  in  the  comments  that  pre-
 scribed burning  is part of good  forest management  practices.

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2.7.4  Preferable to Chemical and Mechanical Methods
     The point  was made by  several  commenters that  the  use  of
prescribed burning  is preferable  to  either chemical or mechani-
cal methods of  land clearing and preparation.  They felt it was
better  to  use  prescribed  burning   from  both  ecological  and
energy standpoints.
2.7.5  Beyond the Intent of Congress
     Several  comments  were  made  that  the  regulation of  pre-
scribed  burning was  beyond the  intent of  Congress  in Section
169A of the Act.
2.7.6  Fire-Natural
     The point  was made that fire is natural to all  areas where
prescribed burning is practiced and that part of the smoke pro-
duced  should be considered natural background.

2.8  PHASED APPROACH
     As  stated  in  the  preamble,  the Agency has  taken a phased
approach to  visibility protection.  These regulations  limit the
scope  of the program to Phase  I  or  to obvious forms of  impair-
ment.  This  approach was  favored  by  most commenters.
2.8.1  Does  Not Provide Adectuate  Time for  SIP Development or
       BART
     The inclusion of  specific time  requirements  for SIP devel-
opment  and  for  BART  was  questioned by  some  commenters  while
others felt that the time  allowed and the substance  in the pro-
posed regulation were adequate.
2.8.2   Specific Date for Phase II
      Some comments suggested  that a specific.date for Phase  II
 regulations should be promulgated.
                                 10

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2.9  TECHNICAL GUIDANCE
     The Agency has issued technical guideline documents in con-
nection with the  proposed regulations,  and received a number of
comments on these guidelines.   The guidelines discuss modeling,
monitoring, and BART.
2.9.1  Modeling
     Comments  were  made  concerning  the  currently  available
models  for visibility  and  the EPA  guideline.   Many  of  these
comments  dealt   specifically  with  the  limitations  of  these
models.
2.9.2  Monitoring
     Comments  were  made  concerning  the  currently  available
visibility monitoring techniques and the EPA guideline.
2.9.3  Lack of Technical Tools
     Several  commenters  felt  the present  tools  available  to
assess or predict visibility impairment are not adequate.

2.10  NEW SOURCE  REVIEW
     Section  51.307 of  the  proposed regulations  deal with new
source review and requirements  for visibility protection.
2.10.1  Lack of Coordination
     There is a requirement for a  State plan in which  provisions
must be made  for coordination with the Federal Land Managers on
certain aspects of  the ne.w source  permit application.  Some com-
menters  felt that  the  procedures for  the coordination between
the  FLMs  and the States were  not clearly defined leaving some
uncertainty on  the order and type of actions each should or may
take in the new source review process.
2.10.2  Inconsistancies  in Definitions
     Some  commenters felt there were inconsistancies  in defini-
tions  for  "adverse impact"  and  for  other  terms as they are.
applied to the PSD  program.
                                11

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2.10.3  Tools to Implement Provisions Dealing with Impact on
        Visibility
     There were comments concerning the availability and useful-
ness of guidance documents to predict and evaluate the impact on
visibility by proposed new sources.
2.10.4  Inhibits Growth
     Some  concern was  expressed that,  if the  proposed regula-
tions were implemented for new source review, they would inhibit
growth  and  development.   The  regulations,  as  proposed,  would
complicate new source siting,  and therefore inhibit new growth
and development.
2.10.5  Fugitive Emissions
     There  were  several  comments  concerning the  inclusion of
fugitive emissions in the proposed  regulations.  Some commenters
felt  fugitive emissions should  not be addressed  in this rule-
making.

2.11   COSTS  VERSUS BENEFITS
      There  were several comments on various interpretations of
costs versus  benefits  of  the   visibility  regulations.  These
comments  dealt primarily with benefits to  be  derived  from  the
protection of visibility in mandatory Class I  Federal  areas in
terms of the overall costs.
2.11.1  Assessing Improvement
      Comments were  received relating  to  the ability to  assess
 improvement in visibility impairment and to  what that assessment
would mean.
 2.11.2  Reasonable Attribution
      There  were  comments   dealing with  what  the  "reasonable
 attribution" to visibility may mean in terms of economic impact.
                                 12

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The commenters' concern was primarily with the number of facili-
ties which  may have to install BART.  There  were  comments con-
cerning what benefits could be achieved at given or stated costs
for these sources.
2.11.3  IGF Analysis
     The  "Preliminary Assessment  of  Economic  Impact  of  Visi-
bility Regulations"  (draft Report by  ICF,  Inc.),  was  the sub-
ject  of  several  comments.   Many  aspects  of this  report were
challenged, and critical comments were provided.

2.12  IDENTIFICATION UNDER SECTION 169A(a)(2) OF MANDATORY CLASS
      I FEDERAL AREAS  IN  WHICH VISIBILITY IS AN IMPORTANT VALUE
     A  few commenters  expressed concern over  the November 30,
1979, identification  of mandatory  Class  I Federal area in which
visibility is an important value under Section 169A(a)(2).

2.13  MISCELLANEOUS
     There  were  other topics  commented  on  frequently which did
not fit into the other categories.
2.13.1  NSO's and Visibility
     Section 119  of the  Act  provides  for administrative orders
that  would  postpone  final   compliance  for  certain nonferrous
smelters  with  SO2  emission   limits.   Several  commenters made
statements  on  the  inclusion or exclusion of visibility require-
ments for nonferrous  smelters  in these orders.
2.13.2  Reversibility of Visibility  Impairment
     There  were  comments  on the fact  that visibility impairment
is  a reversible  phenomenon,   as  opposed to  other  types  of air
pollution effects.
2.13.3  Impact on  Future  Class I Areas
     The  possibility of  the  impact of visibility impairment or
the regulation thereof on Class I  areas  identified  in the  future
was presented  by several  commenters.
                                 13

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                            SECTION 3
                  SUMMARY OF COMMENTS BY ISSUE

     The  following tables  contain the comments  summarized for
major "issues.   The left vertical  column of  the  table lists the
commenter  and the  identifying  number for the  comment.   Across
the top of the table is the subissue identified in the comments.
A brief statement was made in the  appropriate column if the com-
ment  appeared to differ with  or  elaborate  on  the  title of the
subissue.  However, if the comment was brief and essentially the
same as the identified subissue only an "x" is provided.
     Not  all  comments  appear in these summary tables, since the
tables deal only with major issues and subissues.  A summary of
all comments by  commenters is in Appendix A.
                                 14

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                            SECTION 4
                   RESPONSE TO MAJOR COMMENTS

     The  following represents the  responses to- the  major  com-
ments  and issues  identified  in Section  2  and summarized  in
Section 3.  A summary of each individual comment by commenter is
in Appendix A.

4.1  DEFINITION OF VISIBILITY IMPAIRMENT
     There  were  many  commenters  which  had  some  reservations
about the  definition  of "visibility impairment."  Although most
commenters  agreed that "human  perceptibility"  was  the  proper
criterion  for defining  "visibility impairment," many objected
that without further quantification, the  term was  vague  or too
subj ective.
     EPA  intends that  "humanly perceptible"  impairment  have a
common sense meaning,  i.e.,  it is impairment that generally can
be  perceived by  people (such  as  park visitors).  While  it is
true  that human  perception of  a change  in visibility  may be
subjective,  it is this very perception by visitors to the manda-
tory Class I Federal areas that Congress sought to protect from
impairment by manmade air pollution.   There has been and still
is  ongoing  documentation  to relate  instrument  measurements to
the human perceptibility factors.   Perceptibility is based upon
many  different  factors,  such  as  the  background and  natural
conditions  and  probably cannot  be defined as  a  single value
under  all circumstances.  Visibility  in terms of reductions in
visual  range and contrast  change have been demonstrated to be
perceptible.  For instance,  documentation of human observations
of  reductions in visual range as small  as  5 percent and a con-
trast  change in  the range of  0.01  to 0.04 have been reported.
                               146

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Current efforts  to describe  visibility impairment in  terms  of
coloration are promising, but are incomplete.   Although several
alternate  definitions  were offered,  the Agency  feels that  at
this  time  the definition  which  was  proposed on  May 22,  1980,
represents the most reasonable and workable of  all the defini-
tions considered  by the Agency.   Those definitions proposed by
commenters did not truely address the issue at hand, the defini-
tion  of visibility impairment,  but dealt more  with methodolo-
gies, such as human observer  panels,  for determining whether or
not  visibility  impairment existed.   The use of  human observer
panels  as  a monitoring device is  discussed below in Section 4.
     A  number  of  commenters  suggested  that  the  definition  of
visibility impairment  should  be  the  same as the  definition of
significant  impairment.   There are a number of  reasons why the
Agency  has rejected this suggestion.   First,  the national goal
calls for the remedying and prevention of any impairment, where-
as  sources may  obtain an  exemption  from BART  if  they  do not
cause  or contribute  to significant  impairment.   Obviously,  by
the  use of  two  different modifiers   for impairment,  Congress
intended  two different meanings.   Congress  chose  to separate
"significant" from "any" in  Section  169A of the Act and it is
appropriate that  a  distinction is  made  in the regulations.  Even
the  dissenters  to  §  169A in Congress  recognized this distinc-
tion.   See H.  Rep. No.  95-294,  supra, at 528.   Secondly, any
impairment (perceptible  to  humans)  relates to  any change in
visibility that  might interfere with  the  public's enjoyment,
while significant impairment relates  to how much it interferes
with the public's  enjoyment.   Thus,  the definition  of signifi-
cant impairment  includes considerations of such  factors as when
the  impairment  occurs, where it occurs, and how the visitors'
use  might  be affected  by the  impairment.  Lastly,  while Congress
was   clearly concerned  about  substantial  impairment  and the
visitors'  visual experience  of  the mandatory Class  I areas, it
did  not state that it was only concerned with  substantial im-
pairment.   Congress did,  however, recognize that achievement of
                               147

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the national  visibility  goal  could take  a long time  and that
other  considerations  may  affect  the  ability  to  achieve  the
national  visibility  goal  in  the  near  future.    It  therefore
required the development  of a  long-term strategy which includes
cost,  remaining useful life of the affected source  and other
relevant factors.
     Several commenters noted  the fact that the definition for
"significant impairment"  and "adverse  impact" are very similar.
The  two terms  have two  different  applications  in the regula-
tions.   "Significant impairment,"  for the  purposes  of Section
51.303, applies  to mandatory Class  I Federal areas and existing
sources.   "Adverse impact"  applies  to  any Federal  Class I area
and  new  sources  subject  to  the  PSD  requirements of Section
51.24.  Additionally,  "adverse impact" refers to a single major
stationary  source's  effect on  visibility,  while  "significant
impairment" refers to existing conditions most likely resulting
from  several  sources.   The definitions are  essentially the same
because the  same factors  are to be  considered in the determina-
tions  of whether  a potential  effect  is  an "adverse impact" or
whether an  existing  impairment  is  considered "significant."
      Several  commenters argued that the inability to  determine
natural conditions rendered the definition of visibility  impair-
ment  unworkable.  While the Agency  recognizes that the determi-
nation of natural  conditions,  as defined in this  final  rule, may
be extremely difficult until the current  monitoring research is
complete,  it is important to  remember  that (1) some  knowledge
has  been gained through  current research which can be used and
must  be considered in developing a  monitoring strategy,  and (2)
these rules  address only impairment which is reasonably  attrib-
utable.  The combination  of knowledge  gained and the restriction
to reasonably  attribute  will  enable  the  State to implement  a
visibility protection program even  if  it is admittedly somewhat
limited.   Phase  II of the visibility program will necessarily
require a much more precise determination of what  is visibility
impairment and what are natural conditions.
                               148

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     As explained in the Supplemental Statement to the proposal,
EPA  is including  "contrast"  in the  definition  of  visibility
impairment.  Contrast is  a  directly measurable parameter and is
mathematically  interrelated to  visual  range.   Therefore,  EPA
believes  as  a  legal  matter it  can and  as  a policy  matter it
should include contrast in this definition.

4.2  EXISTING STATIONARY FACILITY
     When  EPA  proposed visibility  regulations  on May 22,  1980,
EPA  had not yet finalized  its  PSD rulemaking  in response to
Alabama Power Co. v. Costle,,13 ERC 1993 (B.C. Cir. 1979).   This
latter rulemaking included,  among other things,  a definition of
the  term  "major stationary  source" under  Section 169(1)  of the
Act  for purposes of PSD review.
     In the  statement accompanying its  definition of "existing
major  stationary source"  in the  May  1980, visibility proposal,
EPA  said that
     [a]ny change in EPA's proposed interpretation of
     section 169(1) for purposes of PSD may affect the
     definition proposed today for visibility [under
     section 169A(g)(7)] unless legal authority and dif-
     fering program objectives would support different
     definitions for each program.  45 FR 34771
EPA  noted that  since Congress  took  the  definition  in Section
169A(g)(7) to  a significant degree from that in Section 169(1),
it  was "appropriate"  to  examine  what Congress  intended  under
Section 169(1).  EPA  noted also that in Alabama Power the Court
of  Appeals had carefully  examined Section 169(1) and concluded
that Congress  gave EPA latitude  to define "source" to reflect,
to  a certain degree,  the purpose  and  structure  of the program
for  which  the definition is  intended.  13 ERC 2040.
     EPA  finalized  its PSD  regulations,  including its proposed
definition of "major  stationary source" under Section  169(1), on
August 7,  1980  (45  FR 52676).   These PSD  regulations changed
somewhat -the definitions proposed  under Section 169(1).  EPA's
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definition  of "existing  stationary  facility"  for purposes  of
this visibility rulemaking  reflects  most,  but not all, of those
changes  in EPA's  PSD  regulations.   EPA  incorporates here  by
reference  its response to  comments  on the PSD  proposal under
Section  169 (I)1  to  the  extent that response  is relevant  to
comments EPA  received on its  proposed  visibility definition of
"existing  major  stationary source."  EPA  discusses the changes
from its visibility proposal and responds to additional comments
below.
     Under Section 169A(b) (2) (A), EPA's  visibility regulations
must require  certain "major stationary sources" to install BART
if  they were "in existence"  on the  Act's date  of enactment
(August  7,  1977)  but had not  been "in  operation" for more than
15  years as of that date.  Although the Act does not  define "in
existence,"   it  does,  in  Section  169A(g)(7),    define   "major
stationary source."   EPA's  proposal  labeled this term "existing
major  stationary  source" in  order  to  avoid confusion with the
definition of major  stationary source in its PSD regulations.
For this  same purpose the  final  regulations  label "existing
stationary,"  facility  for  a  source listed in  Section  169A(g)
 (7).2  No  change has been  proposed  or  promulgated in  this rule-
making for the definition  of  major  stationary source  as  defined
 in the PSD regulations.
      The proposal followed the language  of Section  169A(g)(7),
which defines "major stationary source" as  any  one of a  list  of
 enumerated sources "with the  potential to emit  250 tons  or  more
   S FR  52676  et seq. , especially  52688-52698,  52703  (August 7,
  1980).
  EPA is free to  label  these terms as it pleases "so long as the
  regulatory term  is  defined in a  manner  consistent with statu-
  tory requirements."   See Alabama Power  supra,  13 ERG  at  200,
  n. 28.
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of any  pollutant."3   EPA's interpretation of  this  language ad-
dresses  both  the  term  "potential  to  emit"  and  "stationary
source."
     In  response  to the  Alabama Power court's  decision,  and
consistent with  EPA's September  5,  1979,  proposed  PSD regula-
tions (44 FR 51924), EPA's proposed visibility regulations would
have taken into  account  the application of control equipment in
computing  potential  emissions.   The  proposal noted  that  EPA
would  assume  that a  facility's air  pollution  control equipment
would function in the manner reasonably anticipated.
     EPA is today promulgating this  general  approach, which was
supported by public comments.  Today's rule requires that opera-
tion  of control  equipment be a  federally enforceable require-
ment.  Thus,  a company may receive credit for the application of
control  equipment only to the extent  that the resulting reduc-
tion in emissions is  federally enforceable.  In summary, today's
rule  defines   "potential  to  emit"   as  the  ability  at maximum
design  capacity  to emit air  pollution,  taking into account any
in-place control  equipment.  Design capacity, and thus potential
to emit, may be further limited if control equipment better than
that normally  required  by the applicable SIP is installed and a
correspondingly  more stringent  level  of emissions  control be-
comes  federally enforceable.
     The preamble to  the PSD  regulations (45 FR 52688-9) discus-
ses  in detail  the reasons why today's regulations recognize the
ability  of all  federally enforceable  limitations  to  constrain
o
 One  commenter  complained that EPA's proposal impermissibly re-
 stricted  the pollutants which could satisfy the 250 ton thres-
 hold to  those  "regulated under  the Act."  The Act,  the com-
 menter  noted,  speaks of any pollutant,  not any regulated pol-
 lutant.   Although EPA  would expect little, if any, difference
 in  the  "real  world" effect  under the commenter's preferred de-
 finition  and  the  one  EPA proposed, EPA  has accepted the corn-
 mentor's  point.   An otherwise  qualifying source would thus be
 an  "existing  major  stationary  source"  under today's promulga-
 tion if,  as Section 169A(g)(7) provides,  it has "the potential
 to  emit 250 tons  or more of  any pollutant."
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the potential  to  emit  of  a  stationary source.   That preamble
also  states  the  reasons  why today's  regulations,  like  the
May 22, 1980,  proposal  and the PSD  regulations,  count fugitive
emissions in  determining the annual potential  to  emit.   See 45
FR  52690-52693.   The final definition  of "potential to  emit"
announced today  is similar to that promulgated in the August 7,
1980, PSD and nonattainment plan revisions.
     EPA's  proposed  definition  of  "stationary source" in the
rulemaking was  "any building,  structure, facility, or installa-
tion which  emits or may  emit  any  pollutant regulated under the
Clean  Air Act."   EPA gave  reasons  for  the definition  in the
statement accompanying the proposal.4  There were no significant
objections  to  this definition and EPA is today finalizing it.5
     In May 1980,  EPA proposed  to define "building, structure,
facility, and  installation" as
     any grouping of pollutant emitting  activities which
     is located  on one or more contiguous  or adjacent
     properties  and which is owned or  operated  by  the  same
     person (or  persons  under common control).
EPA also proposed that a source would  be treated as  a  new source
if it was  "reconstructed,"  which was presumed where the  fixed
capital  cost  of the new component exceeds  50 percent  of the
fixed  captial cost of a  comparable  entirely new source.  As the
statement accompanying the May proposal  explained  in detail, EPA
concluded that the proposed definition  of "building,  structure,
facility,  or installation" would  serve  Congressional  intent and
the purposes  of Section 169A adequately  by subjecting to BART
those  activities that were reconstructed between August 7,  1962,
and August 7,  1977, provided they had the potential to emit 250
tons a year or  more  of  any pollutant  and fell  within one of the
listed 28  source  categories.  This followed  from  the proposed
 1See,  also,  the  preamble to the proposed and  final  PSD regula-
  tions .
 5For the reasons set  out in footnote 3,  EPA has deleted the re-
  guirement that  the pollutant  emitted  must be  regulated  under
  the Act.
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definition,  EPA  explained,   "since  'source1 would,  in effect,
mean  any grouping of  pollutant-emitting activities at one  site
and   under  common  control."   (original  emphasis)  45  Federal
Register 34771.6
      In  August 1980,  EPA promulgated  identical definitions  of
"building,  structure,   and  facility" for  PSD and  nonattainment
areas.   These terms  mean "all of  the pollutant-emitting activi-
ties  which belong to  the same industrial  grouping,  are located
on one or more contiguous or adjacent  properties,  and are under
the  control  of  the same  person  (or persons under common  con-
trol)."   (emphasis  added).   By   "pollutant-emitting  activities
which belong to  the  same  industrial grouping," EPA meant those
activities  that  "belong to  the  same 'Major  group'  (i.e., which
have  the same two-digit  code)  as described  in  the Standard In-
dustrial Classification Manual,  .  .  .  ."
      EPA added this requirement of "belonging to the same  indus-
trial grouping"  basically   in  response  to comments  that  the
proposed definitions  would  be  too inclusive because  they would
group sets of activities  at one  site  and  under  common control
.that  are functionally  or operationally  distinct.  Typical  of the
examples cited were:   1)  a  surface  coal  mine  and coal-burning
electrical  generators  that the mine supplies with coal,  and  2) a
primary   aluminum  ore   reduction  plant, an  aluminum fabrication
plant,  and  an   aluminum  reclamation  plant.   Under  the  final
definition, however,   these  nominally  different  sets  of  activi-
ties  would fall  into  a different two-digit category.
      EPA has today adopted  the PSD and nonattainment area defi-
nition of "building,  structure,  and facility" for the visibility
 DBy contrast, EPA intended its proposed PSD definition of source
  to apply only to  all  the activities at a plant, and not to ap-
  ply,  in  addition,  to  any subgroup of those  activities.   45 FR
  52696 (August 7, 1980).
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program.  The reasons .are those given in the preamble to the PSD
and  nonattainment  area promulgation.7   EPA  intends that  its
interpretation of "building, structure, and facility" be identi-
cal to that for "building, structure, facility, or installation"
used for PSD purposes.  See 45 FR 52693-52696  (August 7, 1980).8
     In  the _August 7,  1980,  promulgation,  EPA defined  for PSD
the term "installation" the same as it had "building, structure,
and  facility."   For  nonattainment areas, however,  EPA defined
"installation" to mean "an identifiable piece of process equip-
ment. "   Thus nonattainment  requirements would  apply to  a new
piece  of equipment that would emit  "major"  amounts  of a pollu-
tant  for  which  the  area had  been  designated  nonattainment,
regardless  of any accompanying  emissions offsets at the plant.
Referring  to  Alabama Power, EPA stated  that the   fundamental
difference  between  the  nonattainment  provisions   (which  are
designed to  reduce  emissions) and the PSD provisions (which are
designed  to maintain  air quality within  the applicable incre-
ments)  required  this different approach to defining  the sources
subject to  the  nonattainment  provisions.   45  FR 52693-52698.
 45  FR 52693-52698.   Obviously,  some of the reasons advanced in
 support of the definition are peculiar to the PSD or nonattain-
 ment  programs.   Alternatively,  some of  the  reasons discussed
 that  arguably do not  favor this definition are also peculiar to
 the PSD or  nonattainment programs.  EPA  has  considered those
 differences  and concluded that  a similar definition is never-
 theless warranted for this  rulemaking.   EPA also believes re-
 gulatory uniformity,  where possible, is a virtue.  As discussed
 below, however,  EPA concluded that a difference in legislative
 mandate required a different  definition of "installation" for
 the visibility program and the PSD  program.
 Thus,  for  example,  today's definition of  "secondary emissions"
 is  similar  to the  PSD   definition of  that term.    See 45 FR
 52695-52696.  The  only change from the PSD definition reflects
 the fact  that under  the visibility regulations only existing,
 as  opposed to new,  sources  are  affected  by the definition of
 "secondary emissions."
8
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     For  similar  reasons, as  explained below, EPA  has  promul-
gated a definition of  "installation"  in this rulemaking identi-
cal to  the one promulgated for nonattainment  areas.9   The pri-
mary effect of this nonattainment ("dual") definition of instal-
lation, will  be to subject to BART  review those  major additions
that occurred  between  August 7,  1962,  and August  7,  1977,  at a
plant,   even  if that  plant was  otherwise "grandfathered"  from
BART review (i.e., was "in operation" before August 7, 1962),  if
the addition  had  the potential  to  emit 250 tons  a  year of any
pollutant  and if  the addition itself  fell into one  of the 28
source categories.  Thus,  the addition in 1965  to a powerplant
of  a  fossil-fuel  boiler  of more than  250 million Btu per hour
heat input would  be  subject to BART review if it had the .poten-
tial to emit  greater  than 250 tons a year of any pollutant.  On
the other  hand, the  addition  in 1965 of a reverberatory furnace
would not  be  subject  to BART review, even if  it had the poten-
tial to  emit more than 250 tons a year  of  a  pollutant, unless
the  addition  of  the  fixed capital  cost of  the. reverberatory
furnace  exceeds  50  percent  of the  fixed  capital  cost  of  an
entirely new primary copper smelter,  as provided in the defini-
tion of "reconstruction."  The  difference,  noted  by commenters
representing industry, arises because utility boilers are one of
the  28  source categories listed  in  Section  169A(g)(7),  but
reverberatory  furnaces  are not.  Thus,  a reverberatory furnace
added  in  1965 could  not  be "major,"  unless its  addition  or
modification   amounted  to  a  "reconstruction"  of  the  primary
copper smelter of which it is a part.
     Since  this  definition  of "installation" would subject to
BART  review more projects  than  would the plant-wide definition
used  for  PSD purposes  (including replacement  facilities that
would  not be  subject to  BART review under a plant-wide defini-
tion),  use of the  definition is more  consistent  with  Congres-
sional  intent  regarding the visibility  program.  As  explained in
  EPA has  also  today promulgated  a definition of  "reconstruction"
  that  is  similar  to the  one promulgated  for nonattainment  areas.
  See 45 FR  52703.
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the visibility proposal, Congress structured the program so that
the BART  requirements  would be  an important mechanism  for re-
medying existing visibility impairment.
     The  dual  definition  is  consistent with Alabama Power and
ASARCO Inc. v. EPA,  578  F.2d 319  (B.C.  Cir.  1978).   Alabama
Power held that EPA had broad discretion  to  define the consti-
tuent terms of "source" so as best to effectuate the purposes of
the statute.  Different definitions  of "source" can, therefore,
be  used  for different  sections  of the  statute.   See 13 ERG at
2039.  As EPA discussed in its proposal, a central, statutorily-
stated purpose of the visibility program is to remedy any exist-
ing  impairment of  visibility,  not merely to maintain existing
levels of impairment.   See Section  169A(a)(l).   In fact,  a re-
trofit requirement  can logically be thought of only as a device
to  enhance,  rather  than maintain, an  existing condition.   The
legislative  history  expresses  an   unmistakeable  intent  to
"remedy"  and  "cure" existing levels of visibility  impairment.10
The 15 year grandfather provision was to avoid undue burden and
cost.  As EPA said  in  its proposal:
     Although the BART  analysis itself considers the re-
     maining useful  life of the source,  cost, and other
     factors, Congress  decided that EPA  should not  be
     required by statute to require BART for all sources
     regardless of  age  as  a minimum condition for SIP
     approval.
     Where  a source has had an addition  or reconstruction
     with the potential to emit 250 tons a year of  a pol-
     lutant between August 7, 1962, and  August  7, 1977,
     EPA  believes that the implicit concern of  Congress
     regarding remaining useful life does not apply to the
     new  components  at the site and that, therefore, Con-
     gress did not  intend  to  "grandfather" such additions
     or reconstructions.   Such a  "grandfathering" approach
     would be without  reason  and  could  seriously under-
     mine progress  toward  remedying existing visibility
     impairment.  45 FR 34771-34772.
10
   See,  e.g.,  House Report at 205-206; Conference Report at 155.
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The  dual  definition, therefore,  comports with the  purposes of
Section 169A of the Act.11
     Moreover, Alabama Power and  ASARCO  taken together indicate
that  there is  a  distinction  between  Clean  Air Act  programs
designed  to  enhance air  quality  and  those  designed only to
maintain  air  quality.   In ASARCO,  the Court  of Appeals for the
District  of  Columbia  Circuit struck  down  the definition of
"source"  for  new  source performance standards  (NSPS), which had
employed  a   "bubble"  concept.   An  important  element in  the
court's decision  was its belief  that the "bubble,"  by allowing
emission  units to escape NSPS, was  inconsistent with the purpose
of  NSPS,  which was to  improve  air  quality.  See  578 F.2d at
327-28.   But  in Alabama Power, the same  court  held that for PSD
purposes, EPA may use a "bubble"  approach, precisely because PSD
is  designed to maintain  air quality and, therefore, deals with
"a  significantly  different  regulation  and  statutory  purpose."
12  ERG  at 2044.
      Under  this  analysis,  use   of  a plant-wide  definition to
escape  BART review  is  inappropriate since a central purpose of
the visibility program is to  remedy  existing visibility impair-
ment.   Congress itself  pointed to this stark  distinction between
the PSD and visibility programs.   It found that the  PSD program
would be inadequate  to protect visibility because PSD requires
no  reduction in the emissions  of,  and thus no  improvement from,
existing  sources  currently contributing to  unacceptable  levels
of  visibility impairment.   In addition, Congress believed  that
maintaining air quality  within the Class I  increments could  in
some cases still  result in unacceptable visibility impairment.
Thus, Congress had  to  and did authorize a separate  and distinct
 approach to protect visibility.12
 1:LAs the League of Women Voters said in agreeing with EPA's pro-
  posal regarding reconstructed sources:  "A plant which was con-
  structed in the  1950's  that subsequently has been enlarged,  is
  no longer  the same facility  that Congress intended  to  exempt
  from retrofit requirements."
 12House Report at 205.  As  explained elsewhere  in  this  notice
   and  in  the  visibility proposal,  Congress  intended  that the
   visibility and  PSD programs work  together  to the  degree pos-
   sible.
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     Finally,  promulgation of  the dual  definition  follows the
mandate of Alabama Power which held that, although EPA could not
define  "source"  as  a  combination of  sources,  EPA had  broad
discretion  to define  "building,"  "structure,"  "facility," and
"installation"  to best accomplish the purposes  of the  Act.  13
ERC  at  2039.  This holding contemplates  that  one term  (such as,,
"building")  may be  more  inclusive than another  term  (such as
"installation"),  and so a "building" may  include many "installa-
tions."   In this way,  a  "source"  can,  under  Alabama Power,  be
composed  of  smaller "sources,"  yet not be  a  combination  of
sources.   The  dual  definition  fits  into  Alabama Power,   since
under EPA's definitional  scheme,  a "source"  is either  an  indi-
vidual piece  of process equipment or the  entire plant; it is not
a  combination  of sources.   That  is,  when deciding whether  a
source  is subject to BART  review,  the  reviewing authority must
determine whether an individual piece of  equipment, or the plant
as  a whole,  was "in operation" after  August 7,  1962,  and "in
existence"  on August 7, 1977,  and had the  "potential  to  emit"
250  tons  a year  of any pollutant.  A plant or individual piece
of  equipment meeting  these criteria  is a  "source"  subject to
BART review.  Thus, the plant itself is a source, not a combina-
tion of sources,  although it may contain  smaller  sources.
4.3  RESPONSIBILITIES OF THE FEDERAL LAND MANAGER  (FLM)
     EPA's  proposed regulations required  a State to consult in
many  instances with  the  "affected"  FLM  (i.e.,  the FLM having
authority  over Federal  land to  which  the  State plan applies)
before  making  a  decision regarding  its  visibility protection
program.   EPA explained in  the statement accompanying its pro-
posal  that although the State  would retain final authority for
development and  implementation  of  the  visibility protection
program,  the  State's  decisionmaking should be  informed by the
affected  FLM's opinion since those FLMs would be familiar with
the unique  conditions and  the importance of visibility values to
a visitor's experience in  the areas they manage.

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     EPA received  a good deal  of public comment  on the proper
role of the FLM.   Industry and State commenters complained that
the proposal  created  responsibilities  for  the  FLMs that  went
beyond those  detailed in the Act, and that  in many cases would
intrude on the Act's clear  committment  of  a  decision  to  the
State.  On the  other hand,  environmental commenters and members
of the public urged an expanded role for the FLMs.
     EPA continues  to believe that  although the  State  has pri-
mary  responsibility  for  developing  and implementing the visi-
bility protection  program,  Congress intended that the State's
decisions  be  informed by  the FLM's  recommendation.   This  is
apparent from § 169A(a)(2),  which requires  the Secretary of the
Interior to identify in the first instance the manadatory Class
I Federal  areas in which visibility is an important value, from
§ 169A(c)(3)  which  makes  an exemption from the BART requirement
effective  only  upon  the affected FLM's  concurrence,  and most
manifestly  from §  169A(d)  which  requires  the State to consult
"in person"  with the  affected FLM before the public hearing on
its SIP  revision  under § 169A, and  to include  a  summary of the
FLM's  conclusions  and  recommendations  in  the  notice  to  the
public of  the public hearing.   Congress clearly  felt  that the
FLM's  had a  special  expertise  to  contribute, and wanted that
expertise  to  be considered  in the development and  implementation
of the visibility protection program.  This  makes  sense.  As EPA
observed  in  the  statement accompanying its  proposal,  in order
for the  program to work well, the  FLM  and  the State must work
together.
      Congress recognized that FLM/State cooperation was neces-
sary  not only as noted above in connection with  the visibility
program  in particular, but also in connection with the Act in
general.   Section  121 of  the Act  requires the State,  in carrying
out major  SIP-related requirements of the Act  (including protec-
tion  of  visibility),  to  "provide a  satisfactory  process  of
consultation  with  .  .  .  any Federal Land Manager having author-
ity over Federal land  to which  the  State  plan applies  .  .  .  ."
The conference  committee noted that  it had specifically required
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the Senate to "include the Federal Land Manager in the consulta-
tion process with respect to Federal lands."
     In response  to comments from  industry and States,  but in
keeping with Congress1 desire that the affected FLMs be heard on
State  decisions  regarding  the   lands  they  manage,  the  final
visibility  regulations  delete a  number of the  repeated refer-
ences to  FLM  consultation.13 However,  many of the consultation
requirements  that  have  been deleted  are  subsumed under  the
general provisions,  explicitly  required by  the Act,  that  the
State consult the affected FLMs  on its plan revision before the
public  hearing and notify  the   public of  the affected FLM's
recommendations.   EPA believes  that  none  of the deleted provi-
sions  for consultation are  required  as a  minimum  condition of
plan  approval.   Also, their deletion may  help avoid cumbersome
or unnecessary  FLM consultation  requirements and the appearance
that States are not to be trusted—none of which EPA intended in
its proposal.
     Several  private  citizens  expressed  a  concern  that  the
thirty  day  period for review of  a new  source permit application
by the  Federal  Land Manager was  not  adequate.  These commenters
recommended up  to one  year for the  Federal Land  Manager to
review  the new  source permit.   However,   since the State must
perform an  analysis of the anticipated  visibility impacts on the
Federal Class I  areas  at the same time as it is reviewing the
 13
   In  particular,  EPA has  deleted the proposed requirement that
   the State  document why it  did not  accept the FLM's recommenda-
   tion that  visibility impairment is reasonably  attributable to
   a  source.   This  provision  received  the most  objection from
   State and  industry  commenters.  The  other  role the proposal
   gave the  FLMs  that  received  great  objection from industry
   and  -State commenters   was  to  identify existing  visibility
   impairment in the areas they manage.  EPA  has retained this
   provision,  however,  since under Subpart C of the Act Congress
   gave the FLMs the  role  for characterizing  the impairment in
   the areas  they  manage.    It is the  State,  however,  that de-
   cides whether that impairment is  attributable,  and weighs the
   various  cost and benefit  factors  in  determining the appropri-
   ate remedies under  § 169A.  The  State,  of  course,  may also
   identify impairment.

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permit  application,  the  entire  process may  easily take  up to
ninety  days  based  oil the proposed  regulations.   Although  the
Federal Land  Managers could possibly prepare  a better analysis
if they had one year to review a new source application, in many
cases this would  conflict with existing State laws for the pro-
cessing of permits  which  require that the State approve or deny
the permit within 90  days of its receipt.  In addition, extend-
ing the time period   to  one year would  put a large  burden in
terms of delay and construction costs on any company planning to
construct.
     It is anticipated, however, that prior consultation between
the State, source,  and the Federal Land Manager will take place
before  the  complete  New  Source  Review  permit  application is
filed.   In many  cases preapplication  meetings are  held which
would allow  some  additional  time for consultation even prior to
submitting any formal  information regarding the new source.  The
prior consultation would be beneficial in resolving any poten-
tial  problems which  might arise  concerning visibility  in the
permitting process.   This would  also  alleviate what appears to
be  a rather  tight time  constraint for  all  parties concerned.
     There  were  comments about  a possible  veto power  by the
Federal  Land Manager  over new source  permits for sources which
might  impact on  visibility  in the Federal  Class I  areas or on
the integral  vistas.   This is  mistaken.  The State must consider
any  analysis  performed by the Federal  Land Manager.  There  must
be  consultation between  the Federal  Land Manager and the State
during  the permitting process.  The language  in  the regulations
has  been  changed  from the proposal   in  order  to  clarify the
respective roles  of the Federal Land Manager  and the  State.  In
no  sense,  however,  does the  Federal Land Manager  have veto power
over  the  new source  permit.   Section 165(d)  of the Act gives
final  authority to the State  in  a case where  the Class  I  incre-
ment is not  violated.   However,  the State  may  choose  to  deny the
application,  condition the  permit,  or require visibility moni-
toring   based on  the comments  of the  Federal Land   Manager.
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Furthermore, if the State is not satisfied with the Federal Land
Manager's demonstration  of adverse  impact,  then the State must
give  its reasons  why the State  did not  deny the  new source
permit  application.   Section  165(d),  however,  does  not cover
integral  vistas.   The  protection  required by Section  307  of
these regulations  regarding integral vistas allows the State to
consider cost, energy, and other relevant factors.
     Several commenters  stated the Federal Land Managers should
have  no part  in  the new  source  review process  at all.  These
comments came  from both industry and  States.  As earlier stated,
Section  165(d) of the Clean Air Act clearly  gives the Federal
Land  Manager  an  affirmative  responsibility to protect Federal
Class  I  areas  from  visibility  impairment.    Congress  placed
responsibility with the Federal Land  Managers since they are the
most  familiar with the characteristics  of  the  Class I area and
are charged by law with managing the  areas.
     There  were also  commenters  which  stated  that the Federal
Land  Managers  did not  have  the   technical  expertise  to make
recommendations  or evaluations relating to air quality values.
As noted,  the Federal Land Managers  are the appropriate persons
to make • certain recommendations  since they are responsible for
the Federal Class  I areas.  The Federal Land Managers  also have
experienced staff or access to  expertise  to aid them  in making
the  technical recommendations  and evaluations  which need to be
made  in relation  to  visibility protection.  To the extent af-
fected  Federal Land  Managers  cannot document  their  conclusion
that  a new source would cause an adverse impact on  visibility,
the State is  of course less apt to be satisfied with the  Federal
Land  Managers' demonstrations.
      One commenter was  concerned  that the Federal  Land  Manager
could stop  new  projects  by  identifying  a new integral  vista.
The  identification of a  new integral vista by  the  Federal Land
Manager does  not  affect  the new source unless the  integral vista
was  identified more  than  six months prior to submission of  a
complete permit   application.    Therefore,  the  submission of  a
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complete new source permit  would not be affected by the Federal
Land Manager's  identification of  a new integral  vista.   Close
coordination between the  State  and the source making the appli-
cation will preclude any unforeseen situations which might cause
an  application  to be  considered  incomplete  or unsatisfactory.
     One  commenter  stated  that  the Federal  Land  Manager would
have control over future energy development around Federal Class
I  areas.   The  Federal  Land Manager  will  be responsible  for
characterizing visibility in these areas and identifing integral
vistas, but  it  will  be the State  that makes  the  final decision
to  approve  or disapprove a permit application where the source
may  impact  on  an integral vista  associated with  a mandatory
Class  I  Federal area.   The State  may  consider energy and other
factors in determining the  appropriate degree of protection for
an integral vista under § 169A.
     There  were  several  comments  which expressed  the opinion
that the role of the Federal Land Manager should be strengthened
in  the regulations.   Most  of  these  commenters  were concerned
citizens  and several  were  from  citizen's  groups.   It is felt
that the  role of the  Federal Land  Manager,  as outlined in the
final  regulations,   is a  strong  one,  but to  add to  it would
intrude on  the  authority of the States  as set  forth  in the Act.

4.4  INTEGRAL VISTAS
4.4.1  Summary
     Under  the  authority of Section 169A, the  final  regulations
require the  States  to protect the  integral vistas of any manda-
tory  Class  I Federal  area  from visibility impairment caused by
new or existing  sources.   This protection must  be  adequate to
make  reasonable  progress  toward  the  national visibility goal
over  10-15  years considering the cost  of  compliance, the time
necessary for compliance, the energy and nonair quality environ-
mental impacts of compliance,  the remaining useful  life of the
 source,  and the degree of  improvement in visibility anticipated
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to  result  from  control.   A State  in its initial  SIP  revision
would have to protect  an integral vista only if it was  notified
of  the  integral vista at  least six months  before  plan submis-
sion.   With  regard to permitting new sources,  integral  vistas
identified at  least six months before submission of a  complete
permit  application would have  to  be protected.  Under the final
regulations,  integral vistas are  not protected under the provi-
sions of Section 165(d).
4.4.2  EPA's Proposal
     The proposed regulations  would have required a  State  to
protect  any integral  vista—defined  as  a  view from  within  a
Class  I area  of a scenic landmark located outside  the  area's
boundary—identified by  the  Federal Land Manager within 90 days
of promulgation, unless the State in its SIP demonstrated to the
Administrator that the Federal Land Manager did not identify the
integral vista according  to  certain criteria EPA  proposed for
comment.  A  vista identified  by  the Federal  Land  Manager more
than  90 days after promulgation  would under  the  proposal have
had to  have  been protected from visibility impairment not later
than  at the  time of the periodic review of the long-term strat-
egy.
      In its  statement that accompanied the proposed regulations,
EPA described in detail  its approach to integral vistas, as well
as  alternatives  to the  proposed  approach.   See  45 FR 34775-
34776.  EPA  recognized that the issue would be controversial on
both policy  and legal grounds.
      Specifically,  with  respect to  the  legal  authority for its
position, EPA  noted that  it was  aware of comment that Congress
did  not  intend  to   protect  integral  vistas  under  Section
169A(a)(l) which limits  the geographic extent of the visibility
to  be protected to that  "in" mandatory  Class I Federal areas.
EPA replied  that protecting  integral vistas under authority of
Section 169A(a)(l) was 1)  consistent with the  statutory language
because visibility is a perceptual value that  occurs  "in" the
Class  I area;  and 2)  supported  by the  legislative history of
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Section 169A  and much of  the  legislation creating  the  Class I
areas,  both of  which  allude  to  Congress1   desire  to  protect
extensive vistas and expansive scenic views.
4.4.3  Public Comment
     No single  aspect of  EPA's  proposal received more  comment
than this issue  of integral vistas.   A large number of individ-
uals  supported  protection  of  integral vistas  (many also urged
protection  for views  from  outside the Class I area looking into
the  area),  as did several  environmental  groups and  the  Depart-
ment  of the. Interior.  These persons noted that  one's views
while  in  an area do not stop  artificially at the area's perim-
eter,  and  that  the  ability  to  see  distant objects is often
central to  the  visitor's  enjoyment  of an area.   These  persons
did  not,  however,  make  any  significant  arguments  as to EPA's
legal  authority  to protect such vistas under Section 169A other
than  to cite with  approval the rationale EPA  set out with its
proposal.
     Other  commenters,  including most  of   those   representing
States  and  industry,  opposed  the requirement for protection of
integral vistas.14  They argued that Section 169A provides only
for  visibility protection  "in" mandatory Class I Federal areas,
and  by definition  objects of  integral vistas  lie  outside the
area.   Since  Congress was  obviously concerned with  limiting its
untested, potentially costly visibility  program,  it would make
no  sense,  these  commenters  said,  to infer  that  Congress  by
implication intended  to  protect integral  vistas  and   thereby
dramatically  increase  the land  area  to which  the visibility
regulations would  apply.
      Congress,   it  was  argued,   referred  directly  to  adjacent
areas  (as in  Section  165(e)) when it,  in  fact,  had them  in mind.
Here,  Congress expressly precluded in Section 169A(e)  a  require-
ment for uniform  buffer zones.   Finally, since such  regulation
 14
  The United  States  Department  of Agriculture  and the United
   States  Department  of  Energy also  opposed this  requirement.

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would subject non-Federal lands to Federal land use restrictions
without  any express grant  of authority by  Congress,  constitu-
tional  issues  of  state  sovereignty would  be raised  under the
tenth amendment, as well as issues of compensation for taking of
private land under the fifth amendment.
     These commenters also expressed policy reasons for opposing
required  protection for  integral  vistas.   A requirement  that
integral  vistas be protected under § 165(d) could,  they said,
greatly expand the number of new facilities affected, the number
of  prime  sites  (including  prime  sites  for  energy-producing
facilities)  foreclosed,  and  the  incremental  costs  for  new
sources.   This  would  result  they  contended,   because*  under
§ 165(d)(2)(C)(ii)  a  permit would  have  to be denied  if an ad-
verse  impact of- an integral  vista would result.  Additionally,
some States  objected  to what they viewed as undue intrusions by
EPA into  the traditional  State area of land use regulation.  At
the  same  time,  however,  many  industry  and  State  commenters,
while  disputing the authority and wisdom of protecting integral
vistas  under Section 169A, recognized that there may be areas
outside  mandatory Class I  Federal  areas  where visibility is an
important aesthetic value  and should be protected.  If integral
vistas  are  to be  protected,  these commenters  concluded,  the
States  should  be allowed to balance competing interests  such as
energy and economic concerns.
4.4.4   EPA's Response
     After careful review  of the extensive comments sought and
received  on this  issue,  the Administrator  has  determined that
Congress  did intend that the States protect the integral vistas
of  mandatory  Class  I Federal  areas under  §  169A.   EPA agrees
with  the industry  and  State  commenters to  the  extent that the
State,  in determining the appropriate measure of protection for
any integral vista, may consider  competing interests such as the
cost  and energy  effects.   This is because protection for inte-
gral   vistas   is   authorized  and   being  required  under  Section
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169A—which  requires  only  that  "reasonable  progress"  (a  term
that  allows  "balancing"  of  interests)  towards  the  national
visibility goal be assured and not, as originally proposed,  also
under § 165.
     For the  reasons  set out  in  the  statement accompanying its
proposal*. EPA  believes  visibility  "in"  (§  169A(a)(l))  a manda-
tory  Class  I  Federal  area includes  integral  vistas.   Although
§ 165(d) speaks  of the  air  quality  related  values  (including
visibility)  "of"  a Federal  Class  I  area,  in light  of public
comments the  Administrator has concluded that Congress did not
under § 165 intend  similar protection of integral vistas.  This
different interpretation is based on legislative history and the
statutory  framework indicating Congress'  intent that  the  sub-
stantive requirements  of Section  169A be a "separate approach"
from that in  Section  165,  which deals with the PSD program.  H.
Rep. No. 95-294, 95th Cong.,  1st Sess. at 205.
     Visibility protection in the PSD program is under § 165(d).
This  language in  § 165(d)  concerning the  "air quality-related
values  (including  visibility) of a Class I area"  came from the
1977  Senate bill.   Neither the 1976  nor 1977 Senate bill,  how-
ever, contained the parenthetical reference to visibility as an
air  quality-related value.   In fact, neither the  1976 Senate
Report  nor  the 1976 Conference Report discussed visibility as a
protected value.   The  parenthetical inclusion of visibility was
only  added  in conference in 1977.  By contrast, § 169A was pre-
sent  in the 1977  House  bill, and  was  fully  considered by both
the  House  and conference  committee.   It,  therefore,  appears to
the  Administrator  that  the  careful  policy  considerations and
choices made  by Congress in § 165(d), which were limited to the
physical boundaries of Class  I areas, focused on air quality-re-
lated values  apart from visibility, and that by adding visibil-
ity  to  § 165(d) Congress  did not  intend to  extend coverage of
that  provision beyond the geographic boundaries  of the areas.
It is unlikely that Congress  intended to include integral vistas
by use  of that term.
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     This conclusion is also supported by the stringent require-
ment  in Section  165(d) (2)(C)(ii)  that the  State  deny a  PSD
permit  to  construct if it is  satisfied with the  Federal  Land
Manager's demonstration that an  adverse impact  on air quality-
related values  would result.  As the  Senate  report shows,  Con-
gress  was   aware  that  with this  provision  it  was  giving  the
Federal Land Managers  a "powerful tool" which should be wielded
"aggressive[ly]" to  "protect the air quality-related values for
future  generations."   S.  Rep.  No. 95-127,  95th Cong., 1st Sess.
at 36.  To  conclude that in this section,  Congress contemplated
that  integral vistas were protected as part of the Class I area
ignores the origin of  this  language,  and  would thereby greatly
magnify  the potential  effect  of an  already  powerful statutory
provision.  The Administrator believes, rather, that Section 165
represents  a deliberate balancing by Congress of air quality-re-
lated values  (apart from visibility)  and  other  factors, a bal-
ancing premised on the  known geography  and boundaries of Class  I
areas,  which did  not  include  the concept of integral vistas.
      In § 169A, by contrast,  Congress was focusing specifically
on visibility,  and had the  occasion  to make  the policy choices
and balances with respect to visibility in particular.  As noted
in  the proposal  (45  Federal  Register 34776),  the  legislative
history of § 169A  indicates that in making  these choices Con-
gress did  include  protection of integral vistas  of mandatory
Class I  Federal  areas.   The balance  it struck,  however,  was
different  from that  in § 165(d).  Instead  of deciding conclu-
sively that air quality related values within the boundaries of
these  areas  could  not be  adversely  affected   [§ 165(d)(2)(c)
(ii)],  Congress in  §  169A  provided for protection of all visi-
bility values  in  mandatory  Class  I  Federal  areas  (including
integral  vistas),  but  limited  the protection by requiring only
reasonable  progress towards  the national goal,  and by leaving
the balancing to  the SIP process under §  169A.  Unlike  the con-
clusive balance of  §  165(d)(2)(c)(ii),  the  reasonable  progress
criterion  allows the  State to  balance costs,  energy concerns,
and other factors.
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     This  interpretation  will   not  inappropriately   curtail
energy  or  other economic  development,  as some  commenters  pre-
dicted,  because today's   rule  (unlike  the  proposal)  protects
integral vistas  only  under  § 169A, which  allows the  State to
balance energy and economic costs, among others.
     Because  under  §  169A most  new major  sources will  be re-
viewed  for  their affect  on  integral vistas  previously identi-
fied,  the  situation would not  result,  as EPA  erroneously  sug-
gested  in  the  statement accompanying  its  proposal,  in  such
vistas being  protected by one program under § 169A and impaired
by  another  -under PSD.  Rather,  these  integral vistas will be
protected fully under  § 169A, which covers both existing and new
sources.
     Since the protection these regulations give integral vistas
hardly  amounts to  making  them  "buffer zones,"  let  alone "uni-
form"  buffer  zones,   they  are not precluded  under  § 169A(e).
See,  also,   45 Federal Register  34776.   In response  to other
comments, EPA notes that  since § 169A protects only visibility
"in" an area,  the protected perception must occur in an area and
cannot,  as  many commenters  urged,  include  perceptions  of the
area from outside the  area's boundaries.
     Finally,  since Congress  has  authorized the  protection of
integral  vistas,  and  since  these  regulations  give  the  States
freedom  to  balance energy,  economic and other relevant  factors
regarding the measure  of  protection afforded, the Administrator
does not  believe that the arguments of one commenter concerning
the  constitutional  issues that would be raised if such were not
the  case now  raise  serious  questions.   See e.g., McCoy-Elkhorn
Coal Corp v.  EPA,  —F.2d.—  (6th  Cir.  6/2/80)  regarding  Con-
gress1  authority under the commerce clause.  In particular, the
Administrator notes that,  without violating the Fifth Amendment,
the  Federal  government may  execute laws that  affect economic
values or  property interests.   As  the United  States  Supreme
Court  said  in Penn  Central Trans. Co. v. New York City, 438 U.S.
104,  124 (1978), a taking is unlikely when "interference  [with
property] arises from  some public program adjusting the benefits
and burdens  of economic life to promote  the  common good."
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4.4.5  How It Works
     Today's  promulgation allows  the  Federal  Land Manager  to
identify  "integral vistas"  according  to  criteria  the  Federal
Land Manager  develops.   Any  integral vista must be important to
the visitor's visual experience of the area.
     In response to numerous comments that.the public should be
able  to participate in this identification process,  the final
rule requires notice to the public and an opportunity for public
comment  regarding  the  criteria  for  identifying  an  integral
vista.  After the Federal  Land Manager identifies  an integral
vista,  the Federal Land Manager must notify the State.   Unless
the State  determines that the Federal Land Manager's identifica-
tion  was   not in accordance  with  the criteria,  the State must
list  the  integral  vista in  its SIP,  and require in its revised
plan measures that would protect from visibility  impairment any
integral vista the Federal Land Manager identified  at least six
months  before plan submission.  Any integral vista the Federal
Land  Manager  identified  later would have to be  listed  in the
State  plan at the earliest  opportunity,  unless the State found
the identification unreasonable.
     The  State plan must  also  protect the visibility values of
any  integral vista from  impairment caused by  a new source re-
viewed under § 51.307  of  the final regulations where the inte-
gral  vista was identified at least  six months before submission
of a  complete permit application.   EPA has  added this six months
notification requirement in  response to comments that it would
allow time for the business planning proposed new sources need.
Any  shorter  period  would create  too much uncertainty  for new
sources.
      EPA  also proposed that no integral vistas  could be  identi-
fied  after December 31, 1985, by which  time  EPA was advised the
Federal Land Managers would have completed their development of
certain area management plans which could  lead  to identification
of additional integral vistas.  EPA  is  retaining this provision
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in response  to  comments that  it  provides  additional certainity
for new sources.
     Since,  as  noted above,  the  requirement for  protection of
integral  vistas comes  from  Section 169A,  measures the  State
adopts to  protect  such vistas may  reflect  consideration of the
costs  of  compliance,  the  time  necessary  for  compliance,  the
energy and nonair  quality  environmental  impacts of compliance,
and the  remaining  useful life of any affected  existing source
and equipment therein.

4.5  LONG-TERM STRATEGIES
     Some  of the  commenters  felt  the periodic review of the
long-term  strategy  should be every  five years  instead  of every
three  years.  The  Agency believes  that research and technology
is  progressing   so  rapidly  in the  area  of visibility cause,
measurement, and control that three years  is  a reasonable time
period  to review the State Implementation Plan.   Congress was
vitally  concerned  that progress  toward the national visibility
goal begin as  soon  as  possible.   See H.  Rep.  95-294,  supra at
206.   What  is   required  is review, not  total  revision,  every
three  years.  This  review may suggest that only a partial revi-
sion to the  State's visibility regulations is appropriate.
     One  commenter  suggested that  the affect  of new sources on
visibility in the mandatory Class I Federal area, as required by
the  long-term   strategy,  should  not be  affected  by visibility
impairment caused by sources  which existed prior to August 7,
1977.   In particular, this commenter said, the  long-term strat-
egy should not be affected by sources causing visibility impair-
ment which existed prior to August  7, 1962, and which are there-
fore  exempt from mandatory  application of BART.  It is reason-
able   and  necessary,  however,  to  consider present visibility
impairment in planning  and  developing a SIP and  in the long-term
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planning in order to make reasonable movement toward the nation-
al visibility goal,  and there is no basis in the Act for ignor-
ing  these  sources.   Under Section  169A(b)(2)  of the  Act,  the
visibility regulations  must "...require  each  applicable imple-
mentation  plan  for  a  State  ... to  contain  such  emission
limits,  schedules  of compliance,  and  other measures as  may be
necessary  to  make reasonable progress. .  .  ."   To consider new
sources  in the  absence  of  existing  sources  would lead  to  a
confusing, misdirected  program that would not assure reasonable
progress  toward the  national visibility  goal,  as  the Act re-
quires.  Although  such  sources are not subject to the mandatory
BART  requirement,  they may  need to be controlled to make rea-
sonable progress toward the national visibility goal.
     One  commenter stated  that parties other,  than  the Federal
Land Managers should be consulted  during review of the  long-term
strategy.  Before  any SIP could be revised there would, however,
be  a public  comment period and  a  public hearing where  a citizen
or  industrial  representative could comment on the SIP  revision.
There  is nothing in the regulation  to prohibit participation by
a person or group  in  the SIP  revision process.
     One commenter said the  long-term strategy unduly interferes
with State prerogatives.   In  fact,  the  visibility regulations
give the States a great deal of flexibility in determining the
measures they choose  to assure reasonable  progress toward the
national visibility  goal.  As the  Act requires, EPA  has provided
measures for the  States to  consider,  but left the  actual  "mix"
of  measures adopted  to  the  States'  discretion.

4.6 BEST  AVAILABLE  RETROFIT TECHNOLOGY
     A number of  comments were received  on the concept of  Best
Available  Retrofit Technology  (BART).   This is part of  Section
51.302 dealing  with State  Implementation  Plan  (SIP)  revision
requirements.
      Several  members   of  the  public,  industry,   and  agencies
complained that the SIP revision  cannot  be  accomplished in nine
months as  the regulations  require.  The nine month time frame  is
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manadatory  (Section  406(d)(2)(B))  in  the  Clean  Air Act  (CAA)
amendments  of  1977.   Therefore this time  cannot  be extended by
rulemaking.  Although  EPA recognizes  that the nine  month time
period  is  tight,  States  should be able  to  meet  it given  the
limited scope  of this first phase  of  the visibility protection
program.
     Several commenters  were concerned  that  cost  would not be
considered  in  the BART analysis.   In  fact the BART guidelines,
Part I and Part II, as well as the regulations, require retrofit
costs to be considered.   In addition,  Section 51.302(c)(4)(iii)
states:  "If" the State determines that technological or economic
limitations...to a particular existing stationary facility would
make the  imposition of an emission standard  infeasible it  may
...instead  prescribe  a  design,  equipment,  work  practice,  or
other  operational  standard,  or  combination thereof,  to require
the application of BART."  Costs will be determined on a case by
case basis.
     One element of EPA's proposed long-term strategy was that
the State must review the  affects on visibility of  any pollutant
emitted by  an  existing major stationary source when the Admini-
strator determined that new  technology  is reasonably available
to  control  emissions of  that pollutant.  The  State  would then
have to set an  emission^ limitation representing BART  for that
pollutant  if no control  had previously been  required  for that
pollutant  pursuant to  a   BART  analysis.  EPA  explained  in  the
statement  accompanying its  proposal  that the purpose of  the
requirement for review was  to  ensure that States  consider  new
technology  as it becomes reasonably available.  In  addition,  EPA
discussed   some  problems  with  its proposed  approach,   listed
alternative approaches, and  encouraged commenters to  discuss the
legal  and policy bases for any alternative  they would recommend.
     Most  commenters did  not address  this  issue,  and the  re-
sponse  from those that did  were mixed.   Representatives .  of in-
dustry complained that there was  no authority for the require-
ment   because  1)  once BART  emission limitations   are set,   a
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source's obligation is  limited  to "maintain[ing]" those limita-
tions,  § 169A(b)(2)(A),  2) the  clear implication from  the  re-
quirement in  §  169A for BART  and long-term strategies  is  that
BART is independent of the latter requirement and, once imposed,
a  state cannot  be forced to  impose new limitations  under  its
long-term strategy; and 3) where Congress wanted reanalysis, as
in  § lll(b)(l)(B), it  said  so  explicitly.   In  addition,  one
State complained that the requirement would be a "moving target"
that  would  subject sources to  uncertainty.  On the  other hand,
representatives  of environmental groups  supported the require-
ment, as did several other members  of the public.
      Today's  rule  retains the  requirements  that the State must
reanalyze for BART each pollutant for which no control under the
visibility  program has previously  been required.  The require-
ment is  merely  a  recognition  that  certain  emission control
devices for a pollutant like NOX that  contributes to visibility
impairment  may  not be available  now, but may be  available later.
The  requirement is not  one of  "re-BARTing," but  is simply one of
timing  the  initial imposition of control representing BART.  The
requirement has been moved from the section on  long-term strate-
gies to the section on  BART requirements to clarify  this.
      Today's  rule, unlike the proposal, does not require that  a
pollutant  for which a  BART  emission limitation has been set be
reviewed when the  Administrator determines  that new, more-effec-
tive control  technology for the  pollutant  is reasonably availa-
ble. The proposal did  require  a review in  such a case  because  a
State would be  free  under § 116 to require additional  controls
for a  pollutant even where  BART had previously been  determined
for the pollutant.   Today's  rule omits this requirement in re-
sponse  to  comments  and to eliminate the above-mentioned confu-
sion regarding "re-BARTing."  In addition, EPA believes the Act
does not mandate  such  a requirement  as  a minimum  condition  of
plan approval.   EPA continues  to believe that  review  and, where,
 appropriate,  recalculation of the  BART emission limitation  when
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the Administrator  determines  new control  technology is reason-
ably available could be  a good measure for a State, in it's dis-
cretion, to adopt  as part of its long-term strategy, regardless
of the control history of the pollutant of concern.
     Some commenters suggested that the  State  periodically re-
view existing stationary facilities  to determine  if  new tech-
nology is applicable.  The  Agency does not believe that this is
appropriate because a  substantial burden would  be placed on the
State to examine new technology, whereas the Administrator, under
Section 111  of the Clean Air Act is  already charged with this
responsibility.   The   Agency  expects  that the  Administrator's
decision to  call for .reanalysis  will  be usually  based on pro-
mulgation of  additional  new source  performance  standards and on
an  analysis  of  their  applicability  to  existing  stationary
sources.

4.7  PRESCRIBED BURNING
     Many comments were  received  concerning prescribed burning.
Almost  all  the  comments received were opposed to  any further
regulation of prescribed burning.  It was argued that prescribed
burning is  not a major  source, is preferable  to  wildfires, is
part of  good forest management,  and is preferable  to chemical
and mechanical methods  of  land preparation.  .Fire,  these com-
menters noted, is part of the natural background, and regulation
of prescribed burning was not intended by Congress.
     Although the Agency agrees that forest fires occur natural-
ly r prescribed burning by definition is accomplished by man for
the purpose  of conducting  business.   Much of the  forestry in-
dustry  burns  the  nonuseful portion of  trees after harvesting.
Agricultural  burning   is  also  accomplished  for  the  purpose of
preparing fields for use by man.  Since these are done primarily
for man's convenience  and indeed to man's advantage, prescribed
burning must be considered  a manmade cause of visibility impair-
ment.
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     EPA continues  to  recognize,  however,  that  prescribed fire
is an  ecologically sound forest  and management tool  used both
inside and  outside Class I  areas.   The Agency  does  not intend
that prescribed burning be eliminated or unnecessarily restrict-
ed, but only that its affects on visibility be reduced where the
State  determines  it  is  feasible  and  appropriate  to  do  so.
Specifically, the final visibility regulations require the State
to consider the impact of  prescribed burning on  visibility in
the mandatory Class I  Federal area and to examine, and adopt if
necessary,  regulations which  would define the  most efficient,
environmentally  sound  methods  for disposing of agricultural and
forest  wastes  so   as  to  reduce  the effect  of  the  burning on
visibility.
     The requirement for  consideration of prescribed burning is
only  in  the long-term strategy.  As  noted,  the  State must con-
sider  smoke management techniques for agricultural and forestry
management  purposes.   However,  as the comments recommended, the
language  "including such  plans  as  currently exist  within the
State  for  the  purposes"  was  added  to  ensure consideration of
existing  smoke  management  systems  and  regulations.   The long-
term  strategy  requirement  for examination of smoke management
techniques  cannot  be  deleted because  of the  large potential
impact on  visibility  of mandatory Class  I  Federal areas.  As
with  other elements of the long-term strategy,  the  State shall
take  into  account  the costs of  compliance,  nonair quality en-
vironmental impacts and  so on.  Judging  from the comments re-
ceived,  all  these factors  would affect  a management program.

4.8   PHASED APPROACH
      Comments were received from industry, citizens  groups, and
private  citizens  concerning the  phased approach to  regulatory
development  for visibility  impairment. _ Most  of the  comments
favored  the concept itself.   Some  of the  industrial  commenters,
however,  suggested alternate timetables  for Phase  I.   Two  of the
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industry  commenters  felt  more  research should  be  done  even
before Phase  I  rulemaking is promulgated.  Many industries felt
that  EPA  should  postpone  substantive  requirements  for  five
years.  Several commenters even offered schedules for the Agency
to  follow  in the interim until the  final regulations  were pro-
mulgated.  EPA  did not accept  these  suggestions  since there is
sufficient information  and data  available  to start the process
of  developing State Implementation Plans (SIP)  for the control
of  reasonably attributable  visibility impairment.   As  a result,
EPA must not postpone  what  it can  do now  since,  as Congress
recognized, - "if the  [national  visibility]  goal  is ever  to be
achieved, progress  in that direction must  begin  now."  H.  Rep.
No. 95-294, supra, at 206.
     Some  commenters  suggested  that  additional  guidance  is
needed before a BART  analysis under Phase I could be completed.
These commenters  failed to  recognize  the limited scope of these
regulations.   The Agency agrees  that further research  will be
necessary before one can accurately identify and control sources
which cause or contribute to all types of visibility impairment,
but  Phase  I  does  not  require  such  comprehensive  knowledge.
Reasonably attributable impairment can be  addressed now and in
some  cases  controlled without  a  detailed knowledge of  natural
conditions or frequency of impairment, as discussed elsewhere in
this  response.   (It  should be noted,  for example, that while
"significant  impairment"  takes  into account the  frequency of
impairment, a precise forecast  of "frequency" may not be neces-
sary since it is  likely  that any impairment would be considered
significant unless it occurred at such times or such places that
it  did not interfere with the public's enjoyment  of the area).
The phased approach does allow additional  time  for research in
the areas needed.
     Several commenters wanted a specific date for Phase II.  It
is  impossible,  however,  to set a date for  addressing problems
such  as  regional haze and urban plumes until more research has
been conducted and the results evaluated.   The Agency is working
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towards  the development  of  Phase  II  of the  regulations,  but
monitoring  techniques  must  be  improved  in  order to  provide a
data  base on  specific  levels  of visibility impairment  as  the
result of multiple  sources  problems.   Models of complex sources
need  additional research  and are  not available  at  this time.

4.9  TECHNICAL GUIDANCE
     There  were  commenters  who  responded on issues of technical
guidance  for the proposed visibility regulations.  Most of these
comments  addressed  the  modeling and monitoring aspects that are
needed  to  support  or  demonstrate compliance  with regulations
which will  be  developed by  the  States.  There were also comments
by States and  private citizens  that guidance and additional data
were  needed in this area to properly develop  a revision to  the
SIP.
4.9.1  Lack of Technical Tools  and  Scientific Data
      Several  of the State  agencies felt that the cost of moni-
toring and  equipment for the SIP  revisions and  for the long-term
strategy would be  an  excessive  financial burden  on them.   The
mechanism in  §  105 Grant  applications  is  available to  request
additional  funding  from EPA for this  equipment.
      EPA agrees that further research and  additional technical
tools in the  area  of visibility impairment are needed, and is
committed  to  continuing   research  in  order  to  provide these
tools.    However, EPA  feels  the  necessary  technical  tools  are
available now to perform,  within  the  Phase  I program,  a  case-by-
case analysis  on sources  impacting  on visibility of mandatory
Class I Federal  areas  and new sources which may  impact  on
Federal  Class I areas.
4.9.2 Modeling Guidance—Workbook for Estimating Visibility
        Impairment and Users Manual for Plume Visibility  Model
      It  should  be  pointed  out that  although EPA solicited  and
 received comments  on  certain modeling  guidance in  connection
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with  the proposed  regulations,  the  final  regulations  do  not
require  the  State  to use such guidance.   Since  a State may, in
its discretion, use  the  guidance in implementing the visibility
program, EPA has  revised the guidance in response to comments,
and provided the following  discussion of comments on this guid-
ance as well.
     Several  commenters  stated  that  visibility  modeling  is,
inaccurate,   if  not impossible,  in  areas  of  complex terrain and
at distances greater than  50 km  from a  source.   We agree that
the uncertainty  associated  with the use  of  Gaussian models in-
creases  as  the distance from the source  increases and in areas
of complex  terrain.   Modeling of plume dispersion at distances
of up  to 100 km  ideally would consider the spatial and temporal
variations in windspeed,  wind direction,  and  stability that no
doubt have an influence on plume dispersion.   However, as stated
in the Workbook,  data with this kind  of resolution are rarely,
if ever, available because of cost considerations connected with
data  collection.   Since  a   and a   curves  are  derived largely
from  atmospheric  diffusion experiments at  close range,  uncer-
tainties certainly do exist  in their  application at distances
more than 50 km from a source.
     It  is clear that complex terrain  can dramatically influence
plume  transport and dilution.   As noted in the Workbook, complex
terrain  can  result in channeled  or trapped flows and enhanced
plume  dilution due to mechanical turbulence.
     All of  the above notwithstanding, we believe that realistic
estimates of visibility impairment can  be made  using the Work-
book  and PLUVUE model.   Considerable  flexibility is built into
the model so that  the user can account for complex meteorology.
For example, the user can  adjust diffusion  coefficients on the
basis  of measured plume or  tracer data.   Also, the  user  has
other  techniques to account for changes in meteorological condi-
tions.   It  should be noted that none  of the commenters offered
an alternative to the Gaussian model.
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     There were  also several  comments on  the  use of  the  con-
trast/contrast change criterion of 0.1 and the AE(L*a*b*) crite-
rion of  4 for worst-day impacts was  questioned.   If visibility
impairment resulted  in  a  contrast/contrast change of 0.1 on the
worst day in a year, considering typical frequency distributions
of  impact,  one would  expect that perceptible  impairment would
occur, but only  a few days per year.   Thus,  these criteria are
considered  to be  reasonably  conservative  definitions  of  the
magnitude and  frequency of  occurrence of visibility impairment
that would  not be  judged  significant or  adverse.  The criteria
are not  meant  to be interpreted as "perceptibility thresholds."
Modern psychology discounts the notion that  there is a clearly
defined  threshold  below  which  a stimulus  does  not  produce  a
response.
     There were some comments that since Gaussian models  in some
cases  cannot  accurately  predict  ground-level  concentrations,
this  represents   evidence  that plume  visual effects  cannot be
predicted with a Guassian  model.   This argument is not neces-
sarily valid because with  visual  effects  we are concerned pri-
marily with plume  centerline  line-of-sight integrals,.not with
ground-level time-averaged  concentrations.  For typical  line-of-
sight geometries  the visual impact  is  largely independent of the
assumed  plume width (a )  and  is  dependent only  on the  vertical
depth  of the  plume (crz)-   Thus,  several sources of  uncertainty
are eliminated   in  visibility modeling  vis-a-vis  air  quality
                     N.
modeling.
      Several  commenters  stated  that  because  of  approximations
made  to  compute  the diffuse radiation field, the model is  inap-
propriate.   Although diffuse  radiation calculations affect the
absolute intensity  (radiance)  of  the  sky or other viewed object,
the relative  changes  in  sky intensity caused  by air  pollution
are not  sensitive  so  the  accuracy of the diffuse  calculation.
Virtually all of the visibility  impairment parameters  are  rela-
tive  intensity measures (via., contrast,  blue-red ratio, visual
range,  and AE).   Indeed,  recent work suggests that the  simple
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formulas  that  neglect multiple  scattering  are  as  accurate  in
predicting  these relative  measures  as  the more  sophisticated
models.   It should  be noted  that even though calculations are
insensitive to diffuse intensity calculations,  model comparisons
with measured  sky intensities  show that the  diffuse radiation
approximation used in PLUVUE is reasonably accurate.
     One commenter questioned the use of the lowest magnitude of
impact  associated with a  given class of meteorological condi-
tions in  cumulative  frequency distributions.  It is appropriate
to use the lowest magnitude of impact associated with a class of
meteorological  conditions  when  cumulative  frequency distribu-
tions  are plotted.   For example, if  windspeeds  less than 2 m/s
occur  10  percent of the time, we would say that the cumulative
frequency of impacts  greater  than that associated with 2 m/s is
10 percent.  We  would not  select the magnitude associated with,
say, 1 m/s  winds to  characterize  this point on  the cumulative
frequency distributions.
     Finally there  were some comments on  the  assumption that
visual range and ambient ozone concentrations are independent of
windspeed,  wind  direction,   and  stability.   Of course  visual
range  is  not  completely  independent of meteorological condi-
tions.   However, for nonurban  sites visual  range  is  largely
independent of  wind direction and  stability (time  of  day) and
that only at very high  windspeeds  (>10 m/s) does  visual range
decrease,  presumably due to windblown dust.   EPA is not aware of
any studies of the dependence of nonurban ozone concentration on
meteorological  conditions.   Certainly  if  one has  an extensive
data base,  one  would be  advised to  compile  a  five-way joint
frequency distribution of  windspeed,  wind  direction, stability,
ozone  concentration,  and  background  visual range,  and  to use
this joint  frequency distribution to  determine the  frequency of
occurrence of worst-case conditions.
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4.9.3  Monitoring Guidance
     It should be noted that although EPA solicited and received
comments on  certain monitoring guidance  in connection with the
proposed regulations,  the final  regulations  do  not require the
State  to use such guidance.   Since a  State may,  in its discre-
tion,  use  the guidance  in implementing the visibility program,
EPA  has  revised the guidance in  response to comments, and pro-
vided  the  following discussion of  comments on this guidance as
well.
     The majority of comments on  the subject  of^visibility moni-
toring expressed the  opinion that  any  guidance  on visibility
monitoring  was premature.   Many of  these same  commenters be-
lieved the "Interim Guidance  for  Visibility Monitoring" (interim
guidance)  contained  insufficient  information to  establish an
active monitoring program.
     The  interim guidance is  just that  -  interim.   It was not
intended  that  the  document  be a  specific,  all  encompassing
guidance  on  visibility  monitoring.   Rather,  it recommends and
discusses methodologies  and  techniques which  would  be  useful to
those  parties which  desire, or  find  it necessary, to monitor
visibility.   Ongoing  research  programs  sponsored  by EPA and
Federal  land managing agencies,  as well  as  industry, are  col-
lecting  and  evaluating  data  in  an effort to  better define  spe-
cific  techniques  for visibility monitoring.   The Agency's Office
of Research  and Development now has  a program underway  which
would  further evaluate  methodologies  for visibility  monitoring
with the objective of providing definitive  method  descriptions
in up-dated  versions  of the interim  guidance.  These  revisions
would  be released  as  new information becomes available and the
evaluation  progresses.   This progress  would eventually lead to  a
standardized  method   (or methods)  for  visibility monitoring.
     A large number  of  the  comments received  on the  interim
guidance criticized the broad terms  used  to define visibility.
Commenters  described  the definition as "vague" and "subjective."
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EPA believes with  our  present knowledge of visibility a defini-
tion such as this cannot be strictly quantitative.
     One commenter suggested that the  definition  of visibility
as  contained in Webster's  dictionary  be  adopted.  EPA  agrees
that the initial phrase of this definition "the degree or extent
to which something is visible" is an appropriate one to describe
visibility  and  it  has been  included in the  document's defini-
tion.  However,  this commenter infers this definition relates to
or includes that of visual range.  This definition should not be
a surrogate or substitute for visual range.  EPA recognizes that
the appropriate electro-optical parameters that characterize the
perception  of  visual  air quality should  be measured  or moni-
tored, but  this  should not eliminate the use of visual range in
describing  visibility.   Visual range is one  indicator of atmo-
spheric  clarity,   and  because of its historical popularity re-
mains a useful concept for the lay person.
     Another major criticism  of the interim guidance involved
the  apparent lack  of guidance for using human observers to rate
or  characterize  the  perception of visual  air  quality.   EPA
recognizes  the importance of  relating human perception of visual
air  -quality to  measured electro-optical  parameters.   However,
specific  guidance  on  this subject  is  beyond the  scope  of the
interim  guideline.   Ongoing research  programs are addressing
this  problem and  evaluating methodologies  for  establishing a
human-observer-based visibility  index.
     One commenter stated that EPA's proposed visibility program
missed  the essential  point  of visibility  protection - the pre-
servation of the public's enjoyment  of  the Class I  Federal  areas
described   in the  Act.   It  was  suggested that  a  quantitative
estimate  of scenic beauty  be used  to  determine what value the
public  places  on a Class I Federal  area.  Therefore, evaluation
of  the  Class I  Federal  area  would be  in terms of public enjoy-
ment rather than visual  air  quality.
      EPA contends  that  "public  enjoyment"  is a  socio-economic
phenomenon!  that  varies   according  to  a person's  demographic
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background,  level of  affluence,  state  of mind,  etc.,  and  an
evaluation  of this nature  cannot,  from our  present regulatory
viewpoint,  be  based  solely on a  measure  of scenic  beauty.
Scenic beauty may play an important part in this evaluation, but
it is certainly not a substitute.
     The same commenter felt that appropriate guidance should be
included  in the interim guidance  for  determining  vista and sky
color.  Research  in this area  has not progressed to the point
that one method is clearly better for characterizing atmospheric
discoloration.  Thus, any guidance in this area is inappropriate
at this time.
     Another  issue  commented  on  frequently  concerned  the ap-
parent  lack of  focus  on Phase I visibility impairment, i.e.,
visible  plumes.   Commenters  felt  the  interim   guidance  only
discussed visibility monitoring as it related to  regional haze.
Section 4 of the document discusses the special case of monitor-
ing visible plumes.
     Several  commenters  suggested  that the physical limitations
of  existing  mathematical  formulisms,  such  as   those  of  the
Kaschmeider  relationship,  and  0.02  as the  contrast threshold,
should be more thoroughly discussed.   It is simply not practical
to  include as part  of the interim  guidance  all  the background
information  available  on the physical and mathematical formulas
and  theories which apply to visibility.   Limitations in mathe-
matical  formulisms  and monitoring  techniques,  along  with any
errors  incurred by their use are discussed in a number of tech-
nical reports.  References are  included for those  readers inter-
ested in  obtaining this background information.
     Several  commenters  stated that the  interim  guidance  is
"prejudicial  toward use  of telephetometers  for  measuring con-
trast."   Others felt the  interim  guidance recommended only the
telephetometer  as  an instrument to measure visibility.   While  a
two-point multi-wavelength  telephetometer was the recommended
instrument  for  determining  contrast,  the telephetometer  was not
the only  instrument evaluated and discussed.  To the contrary,  a
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number of instruments, which  tend to complement each other, are
recommended.  Specifically, nephelometers,  cameras equipped with
color slide film,  fine particulate monitors,  and meteorological
instruments are  discussed as devices  which make up  a complete
visibility  monitoring program.   Federal  or  State agencies  or
industrial  clients who  anticipate  the need  for  a  visibility
monitoring program should evaluate each of these techniques, and
choose those  devices best  suited to  their  specific  monitoring
objectives.
     There was  some discussion on  the use of  photographs  as a
tool in  visibility monitoring.    One  commenter  felt photography
should be used  more quantitatively since it  is  conducive  to
excellent  quality control, and  the results obtained  were  com-
parable  to  those of a telephetometer.   Research  has  shown that
comparable results are not always obtained with photographs.  An
error of at least 10 percent in  measured  contrast has occurred
when using  photographic  techniques.   Therefore,  EPA  recommends
that photography be  used for establishing a  qualitative  data
base,  while  electro-optical instruments   should be  used  for
quantitative measurements.
     Other comments concerning photography as  a method by which
to  evaluate  visibility   dealt  with  the  frequency with  which
photographs should be taken.   EPA  has found  that photographs
taken three times  a day  of the selected vista is sufficient for
most monitoring purposes.  However, the data can be supplemented
by  more  photographs, if the particular situation  warrants it.
However,   the  Agency does believe that the suggested  method  is
more efficient  and will  not  compromise the quality  of the re-
sults .
     Many  comments were  received  concerning  the  limitations  of
measuring surface  meteorological  conditions and using this data
when evaluating  visibility.   EPA  agrees  there  are restrictions
on  the  use of  such  data.   Surface meteorology  should only  be
used  in   conjunction  with  required  data  and  in  special  case
studies.    Conventional meteorological measurements should,  when
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possible, be supplemented by measurements of mixing depths, wind
directions  and speed along the sight path,  as  well as vertical
profiles.  The interim guidance has been amended to reflect this
information.
     Comments  were received  on the potential  use  of airplanes
equipped with monitoring instruments as devices for establishing
whether  plumes  were impacting  a  Federal  Class  I  area.   One
commenter  felt  this  method was  too "exotic"  to be  useful in
determining "reasonable  attribution."   There are several situa-
tions  which could occur where a  plume could  impact  a  Class  I
Federal  area,  but the origin of the plume could not immediately
be  seen.   EPA believes that tracing the plume  in this manner to
determine  its origin is not  "exotic"  and is, in fact, entirely
appropriate.
      It  was  suggested  that  the  interim guidance  did not  ade-
quately  discuss  the volume  scattering function.   The document
has been amended to better describe this  term.  Other  commenters
felt that  measured parameters should relate  directly  to  what an
observer perceives as well as sees. EPA  agrees and the document
has been amended to reflect this  attitude.
      A specific comment  received stated
                                         " N  is not  the  sum of
                                          L» x.
attenuated inherent radiance  and energy scattered by the inter-
vening atmosphere."  The equation is this:
          tNr = V
                       tNoT
  N  is  the  inherent target  radiance  that is  attenuated  by the
 intervening atmosphere  by a fraction T while Nr*  is  the  result
 of atmospheric scattering between  the observer and target (See:
 Reference No .  6  in the  interim guidance ) .   There  are  no other
 contributions.  For simplicity, units were not specifically men-
 tioned and are not necessary for the relative calculations used
 in the document  (See  reference list in the interim guidance for
 more information and detailed discussions).          . .  '
      A  large  majority  of commenters  discussed  the limitations
 associated  with  participate  sampling.   Since  these  comments
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tended to be very specific, a comment/response format seemed the
most  appropriate way  to  address these  comments or  concerns.
Comment:  A sulfate/nitrate  artifact  problem might  contribute
erroneously to apparent particle concentration.
Response:  The production of particles on sample substrates from
gaseous pollutants  (artifact sulfates/nitrates)  can be  a prob-
lem.   Artifact production  is  related  to  factors  such  as  the
nature  of  the  sample  substrate  and  the concentrations  of  the
precursor gaseous  pollutants.   In most of the  visibility pro-
tected areas  the  levels of SO2 and NO  are very low  suggesting
                                      J\,
no  serious  artifact problems.   There  are  protected areas with
high concentrations of  these  gases.   For these situations addi-
tional precautions  in  the choice of treatment of  sampling sub-
strates must  be exercised.   The interim guidance document  was
not written at a level of detail which would allow discussion of
this  problem.   References which  discuss  establishment  of  an
inhalable  particulate   network  are  included  in the  document.
Comment;   There  can  be  an  interpretation  problem  caused  by
occasional  capture  of  large  particles on the small  particle
receptor area (fine particle stage) of a particle sampler.
Response:   Large particles   erroneously  captured on  the  fine
particle stage  can be  minimized by various  operational proce-
dures  for most size segregating samplers.  Again  this .level of
information is beyond the intended scope of the interim guidance
document.  A  reference  which  discusses  fine particulate network
is included in the document.
Comment:  It  is unlikely  that particle data  can  be  of  use in
visibility phenomena because particle sampling is performed at a
point  in  space while visibility is  an integrated measure over
the entire optical path.
Response:   In most  situations there  will be a sufficient number
of  cases where the point measurement  (particle  sample)  will be
representative  of  the  long path array  of particles such that a
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meaningful  relationship  can be  developed.  A  large degree  of
nonhomogeneity would  complicate  or perhaps  defeat this scheme.
However,  a  comparison of telephotometer  (long  path)  and nephe-
lometer (point) data would be one method to identify such situa-
tions  and  avoid  mistaken  assumptions.   Particle sampling  is
important in trying to establish  the  composition,  etc.,  of the
visibility  impairment.  This  in  no way implies that particulate
data  can be related  to  a visibility  impairment  in every case.
Comment;    It  is  virtually  impossible   to  identify  specific
sources   of  particles by  chemical and  morphological  analysis.
Response:  While  it  is  not  always   possible  to  identify the
relative  contributions  of  specific  sources  to  the  particle
loading,  it  is  often possible  to distinguish  various source
types.   For example,  windblown dust is .quite distinctive physi-
cally and chemically from automotive  emissions.   Other distinc-
tive  categories  include vegetative   burning,  smelting,  fossil
fuel  buring facilities  and sea salt.   If a source  category  is
identified   the  specific  source  can  sometimes  be inferred  by
other available  data  or by conducting specially designed  addi-
tional field research.
 Comment;   The guidelines do not include  adequate information on
 the monitoring for chemical speciation  and size  distribution of
 all relevant pollutants.
 Response;   Specific  details  of  a particle  monitoring  effort
 should be  designed for each program.  Factors  such as  the  ex-
 pected nature, persistence and  concentrations  of the pollutants
 of interest must be balanced against practical considerations of
 logistics and budget.  The guidance document was not designed to
 provide  the level of detailed  information necessary to replace
 program  specific monitoring design.
 Comment;   Paragraph  2  on Page 21 of  the monitoring guidance-
 summarizes  particle sampling and analysis techniques but does
 not specify which to use.
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Response;  Somewhat more  specific  guidance is provided on pages
37 and 39.  Detailed guidance is beyond the scope of the interim
guidance  document.   Program  specific  particle monitoring  and
analysis design is recommended.
4.9.4  Best Available Retrofit Technology
PART I
     Numerous comments were received which discussed the lack of
guidance  on  weighing the costs and benefits  of visibility con-
trol.   The  commenters felt  that  specific guidance  beyond that
included in the BART guideline was needed to weigh each relevant
factor and,  specifically, to compare the anticipated improvement
in visibility  with  the cost  of controlling emissions  for that
level of  improvement.  At the same time, however,  many of these
same commenters  argued that  States should have greater discre-
tion under the regulations in making BART determinations.
     It  is,  of  course,  not  possible  to provide  more  specific
guidance  on how  a State  should balance the various BART factors
while simultaneously giving the State more flexibility to strike
the balance as it deems  appropriate in light of local and site-
specific  considerations.   A  strictly  quantitative  approach,
however,  is not  necessarily  the better alternative.  The proce-
dures outlined in Part 1 allow States  to  consider local condi-
tions  and  circumstances in  their BART  decisionmaking.   This
recognizes  States  have  the  'most  complete  knowledge  of  local
factors which would  affect  the BART decision, and retains State
discretion to  consider the factors in  a case-by-case manner as
was  intended  by § 169A.   The  inappropriateness  of  EPA making
these decisions  for  the  States is underscored  by  the fact that
the  empirical  techniques (as  opposed  to models)  recommended in
the BART guideline do not yield the precise quantitative results
that  would  be  helpful   in  making  uniform  judgments   for  all
sources on how the BART factors should be weighed.
     Several commenters  felt the  comparison  photographic  tech-
nique as  discussed  in Part  1 was vague and  subjective, and as
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such would  not be useful in assessing  the  improvement in visi-
bility obtained by retrofitting controls.
     The  comparison  photographic  technique  is  an  empirical
method by which relative improvement in visibility may be asses-
sed.   There are  obviously  limitations  in  the  use  of  the  de-
scribed method.  But, when applied with common sense engineering
judgment, we  feel  this  technique can provide useful information
in evaluating the effect of retrofit controls on improvements in
visibility.   If the State is  uncomfortable with the results of
the  method,  or a  compatible  source  cannot be  located,  other
techniques  and information  should be explored.   The  State can
then assess the comparison technique in the context of all other
available  information  and make  a  decision  as to whether suffi-
ciently  reliable  information  exists  to reasonably estimate the
amount of improvement that  would  result from  a given level of
control.
     A few  commenters suggested  that the techniques described in
the  BART guideline  for fossil  fuel  fired power  plants with a
generating  capacity  in excess  of 750 megawatts are not transfer-
able  to  other  existing major facilities,   and  that the Agency
should provide specific  guidance on  sources r other  than power
plants.
     The Agency feels the  design  of the BART guideline, espe-
cially Part 1, is general enough  to  be useful to sources other
than  power plants.  Although  some of  the  information is power
plant  specific, the  procedures outlined therein  (See:  Figures 1
and  2) may be applied to any  source undergoing  a  BART', analysis.
Part  II  discusses  more specifically  retrofit alternatives for
power  plants,  but  it  too  can provide information  useful to
analyses of  other  sources.   For  example,  the techniques for
evaluating the cost of a retrofit alternative  for a power plant
may  prove  valuable  when  estimating  retrofit  costs  of other
sources.  Finally,  the  conference report  makes clear that EPA
was  to promulgate specific BART guidelines  only for large power
plants,  and  allow the State  greater  discretion in determining
BART for other existing  stationary facilities.
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     On  July 23,  1980,  EPA  announced  the availability  of the
revised BART guidelines.   In these guidelines EPA said, for the
first time,  that "BART for  the majority of  power plants under
consideration  is the  NSPS,"  and that  a  State  would have  to
provide  a  "detailed justification" for  any departure from NSPS
level of control in setting BART.
     Commenters  complained vigorously that 1)  the NSPS  is for
new sources, and EPA did not develop information on retrofitting
technology  during  the  NSPS rulemaking;  2)  BART by statute must
balance costs  against  remaining useful  life,  degree of improve-
ment, etc.,  and  that the  presumption violates this, 3) retrofit
costs are  higher than the costs of installing controls  during
construction of  a  new plant,  4)  it was  unclear what sort  of
"detailed justification" would  overcome  the presumption,  and 5)
by failing  to  state any basis for the presumption, EPA violated
§ 307(d) and precluded meaningful comment.
     The final rule and  guidelines,  in response to the comments
received,  contain  no  presumption that BART  for large  power
plants  is  the  NSPS  level  of control.   Instead,  the  guidelines
state merely that the controls  needed to  meet NSPS  limits for
power  plants  (40  C.F.R.  Part 60,  Subpart Da)  are  reasonably
available to these sources.  If  this would represent more con-
trol than  is required as  BART in a  given case,   EPA could not
disapprove the plan on that basis since under Section 116 of the
Act  a State is free to adopt controls more stringent than those
EPA requires as a minimum.
     If,  on the other hand, a  State  sets as BART  an emission
limitation  less  stringent than the NSPS   level  of  control,  it
must explain in  detail how it weighed the  various BART factors,
and why the emission limit chosen is more  appropriate than that
represented by the NSPS level of control.   In this way, the NSPS
level  of control   serves  not  as a presumption   for  BART,  but
merely  as  a basis  for comparison that  the State should  use in
weighing,  on a  site-specific basis,  the various BART factors.
As  discussed in  Part  II  of both  the proposed  and  final BART
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guideline,  retrofit controls  that  would allow  a large  power
plant to meet the NSPS level of control are,  on an industry-wide
basis,  technologically  feasible  and  can  be  installed,  as  a
general matter,  at  a  cost about 15 percent higher than the cost
of installing the controls  during construction of a new source.
     Part  I of  the  proposed BART  guideline  stated that,  in
determining  BART under  Phase  I  of the visibility  protection
program,  the  State  should  consider  what   controls  might  be
imposed  in  future phases since  "[i]t  may be more feasible for
the source  to  control a 'future phase' visibility impairment in
conjunction with its Phase I requirements than to wait until the
impairment is formally regulated."
     Several commenters  complained  that  this statement contra-
dicted  the  main basis for EPA's  phased  approach,  which is that
at present  it  is not possible to  attribute Phase II impairments
to  a  source or  determine  the  appropriate   controls  needed to
correct  such impairments.
     In  its  proposal,  EPA was concerned  that controls installed
for particulates in Phase I of the visibility protection program
could  be incompatible  with controls  required to  improve SO2-
caused  visibility impairment in  a later phase  of the program.
Therefore,  EPA urged the State  to  decide whether long-run ef-
ficiency and cost-savings  would  result  by  designing  BART for
Phase  I  to be compatible with the  control that might be required
in Phase II.
     EPA continues  to  believe  that  control  for  particulate
emissions installed without consideration of the future need to
control  SO2  emissions could result  in particulate controls that
would  be incompatible  with necessary  SO2  controls.   EPA also
recognizes,  however,  that it is at  present difficult to attrib-
ute  SO2-caused impairment to  a  source and determine the  degree
of  control  necessary to  improve  such impairment.  Accordingly,
EPA has not required a State to  impose  in  Phase I any SO2 con-
trols  as BART  simply because such controls may be required by  a
later phase.
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     The  question  remains  under  this phased  approach  as to
whether  the environment  or regulated  industry  should bear the
risk  that  a  future  phase may  require additional  (e.g.,  SO2)
control.   The  phased approach  significantly defers the obliga-
tion  Congress  imposed  on these major  existing  facilities  that
impair visibility  in  mandatory Class I Federal areas  and  EPA at
present believes that these sources, since they enjoy the bene-
fit of delay that  this phased approach brings them, should  also
bear  any  risk involved  in that approach.   Therefore, the  BART
guideline states that, at present, EPA  would not consider  incom-
patible particulate controls  installed under Phase  I require-
ments  as   justification  for  not  requiring SO2  controls  under
Phase  II.   This issue will, however, be  resolved in the  public
rulemaking  that  will  accompany Phase II  of the  visibility pro-
tection program, and EPA will not make  a final decision until it
promulgates  those  regulations.   EPA is  announcing its tentative
position  now,  however,  in  order  to   give  States and  sources
advance notice of  EPA's current views  so  they can plan accord-
ingly.

PART II
     Comments  on  the technical  aspects of the  guidelines were
received both  prior to proposal through NAPCTAC  and  after pro-
posal of the guidelines through a public comment period.   All of
these  comments were  taken into  account  in promulgating  the
guidance, specified for  fossil  fuel fired power plants as  re-
quired by Section 169A.
     The comments received on the guidelines presentation of the
state  of  the  art  for  retrofit  NO  control  contend that  the
                                    x
document fails  to stress that adverse side effects of combustion
modification may limit attainment of maximum NO  control.   Other
                                               X
comments were  that the  theory  of NOv formation  was not well
                                      X
explained,   and not enough emphasis was placed on  the  fact that
it might not be possible  to  limit NO  emissions  from existing
                                      X
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steam generators to  the  same NOx limits that are achievable for
new steam  generators.   Although EPA believes  these aspects are
adequately addressed, the  guidelines have been revised to allow
State agencies  to  take  the  foregoing  comments  into  account in
making decisions  on the best available retrofit technology for
NO  control.
     It was suggested that the conclusions reached on the lowest
level of NO  emissions that  are achievable by combustion modifi-
cation were insufficiently supported in the document.  Repeating
the basis  for this  conclusion is not  necessary since the data
presented  in the  background  information document for  the new
source  performance  standards promulgated June  11,  1979 is the
data used  in this  guideline.
     The thrust of comments  from the power industry  on  the  cost
of NO   control are that:  1)  the cost  estimates are  inaccurate,
and  2) the  guidelines  fail to take  into account the cost of
derating for NOx control.
     No  data,  however,  were presented  by the power  industry
indicating whether the cost  estimates  were too  high  or  too  low.
If  information had  been provided for  those  power plants where
the  modifications  described  in  the  document have been  imple-
mented, the EPA would have been willing to consider changing the
cost  estimates.  In  the  absence  of  such information  the  EPA
decided to rely on  the  cost estimates  of the  document that were
derived after consultation with the four major power plant steam
generator  manufacturers.  (A related comment was that the guide-
 lines  for  cost estimates should advise State agencies to consult
 steam generator manufacturers  and  other  combustion modification
 experts on cost estimates.   The guidelines  have been revised to
 recommend such action.)
      In Section 2 of the document derating  is  characterized as
 an undesirable NOx  control  technique.   In response to comments,
 additional discussion of the potential cost of derating has been,
 added  to  Section 4.   As discussed in  Section  4,  it  was not
 possible  to  provide guidelines  for  exact determination of the
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cost of derating.  However, all of the primary cost elements are
identified for State agencies to take into account should derat-
ing- be considered.                           ,     ,  .-   ,
     The guidelines were  criticized  for being top simplistic in
specifying the  size of ESP  systems  for various  sulfur  content
coals.  The guidelines  are intended  to provide a basis for best
available retrofit  technology  decisions and are not intended to
be guidelines on how  to accurately size an ESP system.  The EPA
agrees  with  the  comments that coal  sulfur content is  not the
only  factor  to  be considered in sizing  an  ESP system  or  in
choosing between a hot side or a cold side ESP system.   However,
if  the size  and  the cost  guidelines  given  are used,   an ESP
system can be installed that will limit particulate emissions to
a level  less  than  0.03 pounds per million  Btu for the  capital
and annual costs estimated for the coal sulfur contents given in
the guidelines.  This  is because the size  criteria  of  the docu-
ment  are  for  the  most difficult cases  corresponding  to coal
sulfur  content.   The  guidelines have been revised  to  recommend
advice  from  ESP  vendors to  determine  if  smaller  sized ESP
systems might achieve the 0.03 pound per million Btu particulate
control level.
     Other  comments  alleged that the ESP  cost estimates are
inaccurate and  unsupported.   The basis for the  ESP cost esti-
mates  is clearly stated and referenced.  The cost estimates are
derived from those used in support of the new source performance
standards promulgated June 11, 1979.   A  fifteen percent allow-
ance  has  been added  for  the additional cost  of ductwork for a
retrofit ESP system as compared with a new system.  This fifteen
percent allowance was  derived from  analysis  of ductwork cost
estimates provided by Pullman Kellogg Division of Pullman Incor-
porated.  None of the comments included data on the actual costs
of retrofit ESP  systems.   Consequently, the cost estimates were
not revised.
      It was suggested that ESP pressure drop should be 3 inches
of water  rather than 1/2  inch of  water.   After reconsideration
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of the engineering aspects  the  EPA agrees that the 3 inch value
should be  used.  The  guidelines  have been  revised accordingly
and the  cost estimates are  conservative enough to  provide  for
this change.
     The prime comments on  baghouses dealt with  pressure drop
and  cost  estimates.   Commenters  felt pressure drop  estimates
should be increased and that the cost estimates were inaccurate.
Again, no  data were  submitted to indicate if the cost estimates
were too high or too low,  consequently, no changes were made to
the  cost estimates.   Based on  comments  and  analysis of data on
power  plant baghouses, the  estimated pressure drop across bag-
houses  was  increased  from 5  inches  to 10  inches  of water.
Review of  the  cost estimates showed that the cost estimates were
conservative  enough to  accommodate this  change.
     One  comment was  received  suggesting that the size of bag-
houses  required might  be  reduced by electrostatically  charging
the  particulates.   EPA  concluded  that  the  technique  is  not
adequately demonstrated for power plant applications.   However,
this  technique is mentioned but not  recommended  in the  guide-
lines  for State agencies that  might  want to consider  this inno-
vation.
      There were  comments  that  the  guidelines were  incorrectly
limited to  lime and  limestone scrubbing of  low  sulfur  coals.
Consequently, the guidelines were revised to permit  cost esti-
mates for a wide variety  of SO2  control systems  and coal sulfur
contents.   After  this  revision  there  were  comments  that  the
guidelines did not guide  State  agencies on  which SO2  control
process should be selected.  No changes were made regarding  this
latter comment since,  as pointed out in several  other comments,
the factors  that influence the  choice  of' a  S02  control system
 are site  specific.   Consequently, no specific guidance  can  be
 given for this selection.  a
      Regarding comments that the guidelines  should provide for
 spare  systems components,  review of  the  basis  for  the  cost
 estimates  showed that provision had been made  for  spare  key
 components of  the systems.   Consequently, no  changes were made.
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     There were several comments  questioning the reliability of
other S02  control  systems and effectiveness  of  the  S02  control
systems.   The EPA position  on the effectiveness and reliability
of SO2 control  systems is  given  in Appendices  D and E  of the
guidelines.
     There were comments  that dry scrubbing S02 control systems
are  not  demonstrated  on  full scale  power  plant applications.
This agrees with the  EPA  position on the state of demonstration
of dry  scrubbing systems.   Consequently, no  guideline  changes
were made.
     Some  comments  were   received that stated a  particulate
removal system such as a venturi scrubber is not necessary ahead
of  a lime  or  limestone  scrubbing system.   Although the  cost
estimates provide for such systems the guidelines do not require
particulate precleaning in conjunction with SO2 control.
     There  were several  comments about  sludge  disposal.  Some
commenters  pointed  out that 70  percent sludge  solids  content
cannot be  achieved  in all cases.   The document has been revised
to permit  estimates  of sludge generation at both the 50 percent
arid  70 percent  sludge solid content levels.  The viability of a
50  foot  depth  for  sludge  disposal  sites was  also questioned.
The  EPA  agrees  that a 50 foot depth may not always be possible.
Guidelines  are  provided  for estimating  land area requirements
for  a variety of pond depths.
     Several  commenters  noted that  the guideline  did  not take
into account certain  site  specific  cost factors  including 1)
facility  relocations,  2)  stack  modifications,   3)  sludge han-
dling, and 4)  downtime.   The Agency recognizes  that these and
other  such cost  factors  can have a significant effect on the
cost of  installing  and  operating retrofit control equipment.
However,  these costs  are extremely site  specific for  existing
stationary  facilities  and  must  be  addressed on an individual
basis  and may  be  cause  for  choosing  one BART  alternative over
another.
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     In response to .comments that the guidelines did not include
cost estimates  for stacks the  guidelines have been  revised to
include  such cost  estimates.   However,  the  EPA was  unable to
provide  any guidelines  on .how to  determine  when  a  retrofit
system with  a new stack would be a less costly alternative than
a  retrofit system  using the  existing stack.  This  is because
this  kind  of  determination  requires detailed  site  specific
engineering  studies.   Consequently,  no generalizations  can be
made.
     The  guidelines have been  revised to advise State agencies
that water supply  may  be  a problem  especially in arid Western
areas.   Cooling tower blowdown is suggested  as a possible water
source.
4.9.5  Criteria for the  Identification of Integral Vistas
     Several comments were provided which expressed concern  over
the  "Criteria  for the Identification  of  Integral Vistas."   Some
of the  commenters-  believed  that the  guideline  did not provide
precise,  objective and  reproducible  guidelines for  identifying
integral  vistas.  These  commenters went on to point out that the
procedures  for identifying the vistas (1) were  not  clear,  (2)
failed to require that  a docket or some other type of documenta-
tion  be prepared to  support any identification  of an integral
vista,   (3)  failed to  indicate how  certain factors should be
considered or  weighted when  decisions are  made,  and (4)  used
many  undefined or nebulous terms which make  it very  subjective.
     Comments were  also received which indicated  that while  some
of the  concepts  and ideas  in the   guideline  for  identifying
integral vistas had  merit,  the guideline itself should not be
published as an  EPA  document.  While it was acknowledged  that
EPA's  regulations  should  provide the basis  and definition for
the integral vista concept,  once a  definition is  adopted  it  must
be directed to the FLM for implementation.   Therefore,  the FLM
should  take the lead  for the  development of  the criteria and
procedures for identification of integral vistas.
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     The Agency realizes that in some cases the criteria identi-
fied in the guideline for identification of integral vistas does
need some improvement  and  further explanation and that this can
best be handled by the FLM utilizing their knowledge and experi-
ence in  the administration of  lands  within their jurisdiction.
Thus, the  Agency will not  formally issue  the  "Criteria on the
Identification  of  Integral  Vistas."   This  criteria  will  be
developed and  published by the  FLM.   In  response  to comments,
the  final  regulations  require  the  FLM to  give notice  and  a
reasonable  opportunity  for comment on  the criteria for identi-
fication prior to  its  adoption by the FLM.  The Agency believes
that the  FLMs  have the necessary knowledge and experience with
regard to the  lands  within their jurisdiction to develop crite-
ria  that  will  ensure consideration of  all factors  in a reason-
able and definitive manner.

4.10  NEW SOURCE
     EPA's  PSD regulations  require that  a proposed  new major
source  or major modification evaluate  its potential  affect on
visibility  and,  if the State is  satisfied an adverse impact on
the  visibility value  of a  Federal Class  I  area would result,
that the  State deny the PSD permit.  In response to comments on
the Advance Notice of Proposed Rulemaking,  EPA in Section 51.307
of  its  proposal sought  to  clarify  and  expand, in  a limited
fashion,  the  requirements a  State  must meet in reviewing under
the  PSD  program the affects of a new source  on visibility in a
Federal Class  I  area.
     EPA  received  comments  on  its   proposal   that  visibility
issues  concerning  new PSD  sources  must  be handled  under the
procedures  for PSD,  and that if  a  source's impact on visibility
is  considered  in review  of its  PSD  permit application that is
subsequently  granted,  the  source cannot  later  be  subjected to
the  requirements of  Section  169A.   EPA  agrees with both  of these
points as discussed  below.
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     As EPA recognized in the statement accompanying its propos-
al, there  are  several references in the  legislative  history to
Congress1  concern  that visibility  issues  concerning  new  PSD
sources must be handled under  the  procedures for  PSD.   See 45
Federal Register 34778.  The  Conference Report states:   "Issues
with respect to visibility as an air  quality value in  applica-
tion to new sources are to be resolved within the procedures for
prevention  of  significant deterioration."   H. Rep. No. 95-564,
95th Cong. Rec. S 13709 (daily ed. August 4, 1977)  (Statement of
Senator  Muskie).   In a statement  accompanying technical amend-
ments to the Act, Representative Rogers explained the conferees'
intent in including the above provision:
     The conference committee, of course, did not want to
     subject new sources to two separate procedural steps
     under the PSD and visibility provisions.  .  . . But in
     the one-stop permit process for new and modified major
     sources, the substantive criteria  and standards of
     both the PSD and visibility provisions  would have to
     be met.  123 Cong. Rec. H 11958 (Nov. 1,  1977).
     Thus  the  provisions  proposed and promulgated in § 51.307
for  new  sources are  to  be implemented  within a State's PSD
procedures.   The  reason  these  provisions  are   contained  in
§  51.307,  rather than  in §  51.24  with most of the  other PSD
procedures,  is  to  avoid interference  with  the  State's ongoing
efforts  to  adopt approvable PSD regulations  in response to EPA's
August 7,  1980,  final rules  for PSD and so-called "nonattainment
area"  programs.   45  Federal Register 52676.   Promulgation of the
provisions  of  § 51.307 as amendments  to  §  51.24 would, in EPA's
judgment,  unnecessarily  confuse  the issue  of what changes the
States must make to  their PSD regulations  and when.  The changes
required by this visibility rulemaking must be  made  within  nine
months of  the  publication date  of  the visibility regulations,
while  the  changes  to  a  State's SIP  required by  the  August 7,
1980,  promulgation  must be made within nine months  of that  date.
EPA  believes  Congress desired that States  adopt the  PSD program
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as  soon  as possible,  and  that  any  timing  or organization  of
regulations under  Subpart C of the Act that  would hinder State
adoption  of the  PSD program  would  be  inconsistent with  that
intent of Congress.  Thus,  although, as noted,  the provisions
regarding review  of the affect of new sources  on visibility  in
Federal Class I areas promulgated in this visibility rulemaking
are to be codified initially under a different section of title
40, part  51 of  the Code of Federal Regulation,  these provisions
nonetheless  require  such  review only  within the PSD  proce-
dures . * 5
     Specifically,  Section 51.307 establishes  certain  require-
ments  concerning   integral  vistas discussed  elsewhere in  this
statement.   In addition,   this  section  provides  time  periods
during which  1)  the State must notify the Federal Land Manager
of  a permit application  from  a  proposed new major source  that
may affect visibility in  a Federal Class I area,  2) the Federal
Land Manager  may  seek to  demonstrate to the State that  an ad-
verse impact on visibility would result in such area, and 3) the
State  must  give   reasons  why it was  not satisfied with  the
State's demonstration.
     The  issue  regarding  reconsideration under  § 169A  of  a
source granted  a  PSD permit under § 165 was addressed in  this
colloquy regarding the Conference Report:
15
  One commenter raised  the  specter of a source being subject to
  two visibility reviews—one by  EPA and one by the State—that
  would result  if  a State  adopted a visibility protection plan
  before it  took  over  from EPA the PSD program.   Based on its
  extensive  experience  with State plan  revisions,  EPA believes
  the likelihood of such an occurrence is remote to the point of
  being virtually nonexistent.  As noted above, a State must de-
  velop its  PSD program many months before  it must develop its
  visibility protection program.   In addition,  the States have
  had more  experience with the PSD  program  than the visibility
  protection program.
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     Mr.  McClure.   Once a [permit]  .  .  .  has been granted
     to a new source and the question of  visibility has
     been considered as a part of the air quality values
     under the significant deterioration  provisions,  could
     the source be subjected later to the requirement of
     Section [169A]?
     Mr.  Muskie.  It is my understanding  that was not the
     intent of the conferees.
     123 Cong. Rec. S 13709 (daily ed., August 4, 1977).
     Therefore, after a source has received a PSD permit  and the
question  of  the source's potential  affect  on visibility in any
Federal  Class  I  area  has been  considered,  the  source  may not
later be subjected to requirements under § 169A.  EPA notes that
its  PSD  regulations preceded the  1977 Clean Air Act Amendments
did  not require  analysis  of visibility  impacts,  and therefore
any  source granted a PSD permit under those pre-Amendment regu-
lations   is   subject  to  the  requirements  of  the  long-term
strategy.  A State could, of  course, impose under authority of
§ 116  any requirements on  any source,  including  a  source that
has  a  PSD permit, in order to assure reasonable progress toward
the  national visibility goal.   In any event the State plan must
be  adequate to  assure reasonable progress  toward the national
visibility goal.
     EPA's  proposal would require  a State  to review  all new
major  sources for their affects  on  visibility in any area pro-
mulgated under  Section 169A(a)(2).   In  the preamble  EPA ex-
plained  that  this requirement was  necessary because there are
sources  which are  not subject to the PSD regulations'.  Because
of   the  decision  in  Alabama Power  Co.  v.  Costle,  	  F.2d 	
 (No.  78-1006 12/14/79), the PSD regulation  did  not call for the
review of a  new major  source  locating in a  "nonattainment"  area,
even if it  would  impair visibility  in  a § 169A(a)(2) area.   In
the  statement accompanying the proposal  EPA  explained at  length
the  authority  for applying  the long-term  strategy  to  new,  as
well as  existing, sources.   See 45 Federal Register  34777-8.
                               202

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     Commenters did  not focus on the  specific  issue of whether
EPA  could cover  new  major  sources  locating  in nonattainment
areas, but  several did argue that  EPA had  no  authority to re-
quire  anything of new sources under  § 169A.   These commenters
did not,  however,  present  any arguments not discussed by EPA in
its  proposal  (see 45  Federal Register  34777-8)  or discussed
above  in  connection  with PSD  review procedures.  The  short
answer to those who  see no  authority  in  §  169A to control new
sources is that they ignore the major part of the national goal
that calls for the prevention of new impairment.   It would have
been  nonsensical   for  Congress to  create  a visibility program
that  attacks  the  problem  by controlling  older  sources  while
allowing  new  sources  simultaneously to create the problem anew.
As the House Committee wrote  in its  discussion of § 169A, "the
very  difficulty  of  curing  existing  problems  after  the fact
argues strongly for a  strong preventive approach for the future"
H. Rep. No. 95-294, supra,  at  206.
     Section  51.307  of the final regulations  would require (in
addition  to  the review already required by the PSD regulations)
that  any  new major source that locates in a nonattainment area
must be reviewed  for its  affect on visibility impairment.  This
review for such sources would, however, only be  for the source's
affect on  a  mandatory  Class  I  Federal  area   listed  under
§ 169A(a)(2).   Under  40 CFR   51.24,  a PSD source  would be re-
viewed for   its   affect   on  any  Federal  Class  I   area,  as
§ 165(d)(2)  requires.   As  a  factual matter,  review  of such
sources locating  in a nonattainment area is important  and often
critical  to making reasonable progress  toward the national visi-
bility goal.   For example,  in many cases the §  169A(a)(2) areas
lie  close to  nonattainment areas.   Without the requirement in
§ 51.307  of  the   final  regulations,   a major new  source could
locate in the  nonattainment area and escape review  of its  affect
on visibility in  the  § 169A(a)(2) area, even though that  affect
could  be  significant.
                              203

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     The authority  for the review  required by § 51.307  of the
final regulations  stems  from § 169A which,  as  explained above,
calls  for  reasonable progress   toward  preventing  any  future
impairment, and § 161  which authorizes  EPA to adopt under "this
part" any "measures as may be necessary ... to prevent signif-
icant deterioration."  As noted,  "this part" means Part C of the
Act,  which  includes  §  169A,  and  "prevention  of  significant
deterioration" clearly contemplates protection of visibility, as
shown by § 160  and 165.   Indeed,  the United  States  Court of
Appeals  for the District  of Columbia has  specifically contem-
plated  the use  of  such authority to  protect visibility.   In
Alabama Power Company v. Costie,   supra at  13 ERC  58, the court,
in  concluding that the  PSD permit requirements  do  not, on the
basis of § 165,  extend  to  a source locating in a nonattainment
area, stated:
     Section  169A is available to protect visibility in
     Class  I  areas where visibility is an important
     characteristic, and the Administrator may choose
     to  invoke the rulemaking authority granted to him
     by  section 161 to address this problem.
     Since  the authority  to review  the visibility  effects of
these  new  maj ©resources to  be   located  in nonattainment  areas
comes in part from  § 169A,  not §  165(d), any negative effects on
visibility these sources would cause should be understood within
the long-term strategy to make "reasonable  progress" toward the
national visibility  goal  that  §  169A  requires.    "Reasonable
progress"  allows  the  consideration of cost,  energy,  and  other
relevant factors.
 4.11  COST VERSUS  BENEFIT
      Many comments were received regarding the  overall  economic
 impact of the proposed visibility regulations  as compared to  the
 benefits to  be derived.   Many of  the comments indicated that
 virtually no benefit analysis  had been conducted and that since
 visibility was an aesthetic value economics  and energy  concerns
 should be considered.
                               204

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     Commenters did  not focus on the  specific  issue of whether
EPA  could cover  new .major sources  locating  in  nonattainment
areas, but  several did argue  that  EPA had no  authority to re-
quire  anything of new  sources under  § 169A.   These commenters
did not,  however,  present  any arguments not discussed by EPA in
its  proposal  (see 45  Federal Register  34777-8)  or discussed
above  in  connection with PSD  review procedures.  The  short
answer to those who  see no authority  in  § 169A  to control new
sources is that they ignore the major part of the national goal
that calls for the prevention of new impairment.    It would have
been  nonsensical   for Congress to  create  a visibility program
that  attacks  the  problem  by controlling older  sources  while
allowing  new sources  simultaneously to create the problem anew.
As the House Committee wrote  in its  discussion of § 169A, "the
very  difficulty  of  curing existing  problems after  the fact
argues strongly for a strong preventive approach for the future"
H. Rep. No.  95-294, supra,  at  206.                         ,
     Section 51.307  of the  final regulations  would require (in
addition  to  the review  already required by the PSD regulations)
that  any  new major source  that  locates in a nonattainment area
must be reviewed  for its affect on visibility impairment.  This
review for such sources would, however, only be for the source's
affect on   a  mandatory  Class  I  Federal  area   listed  under
§ 169A(a)(2).   Under 40 CFR  51.24,  a PSD source  would be re-
viewed for   its   affect  on  any  Federal  Class   I   area,  as
§ 165(d)(2)  requires.   As  a  factual matter,  review  of such
sources locating  in a nonattainment area  is important  and often
critical  to  making reasonable  progress  toward the national visi-
bility goal.  For example, in many cases  the § 169A(a)(2) areas
lie  close to  nonattainment areas.   Without  the  requirement in
§ 51.307  of  the   final  regulations,   a major new  source could
locate in the  nonattainment area and escape review  of its  affect
on visibility in  the § 169A(a)(2) area, even though that  affect
could  be  significant.
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     The authority  for the review  required by § 51.307  of the
final regulations  stems  from § 169A which,  as  explained above,
calls  for  reasonable progress toward  preventing  any  future
impairment, and § 161  which authorizes EPA to adopt under "this
part" any "measures as may be necessary ... to prevent signif-
icant deterioration.!1  AS noted, "this part" means Part C of the-
Act,  which  includes  §  169A,   and  "prevention  of  significant
deterioration" clearly contemplates protection of visibility, as
shown by § 160  and 165.   Indeed,  the United  States  Court of
Appeals  for the District  of Columbia has  specifically contem-
plated  the use  of  such authority to protect visibility.   In
Alabama Power Company v. Costie, supra at  13 ERC  58, the court,
in  concluding  that the  PSD permit requirements do  not,  on the
basis of § 165,  extend to  a source locating in a nonattainment
area, stated:
     Section 169A is available  to protect visibility in
     Class  I areas where visibility is an important
     characteristic, and the Administrator may choose
     to invoke the rulemaking authority granted to him
     by section 161 to address  this problem.
     Since  the authority  to review  the  visibility  effects of
these  new  major  sources to  be located in nonattainment areas
comes in part from § 169A,  not  § 165(d), any negative effects on
visibility  these sources would  cause should  be understood within
the long-term  strategy to make "reasonable  progress" toward the
national  visibility  goal  that  §  169A requires.   "Reasonable
progress"  allows the  consideration of cost,  energy,  and other
relevant factors.
4.11   COST VERSUS BENEFIT
     Many comments  were received regarding the  overall economic
impact of the proposed  visibility regulations  as compared to the
benefits  to be  derived.  Many  of  the  comments indicated that
virtually no benefit analysis had been  conducted and  that since
visibility was  an aesthetic value economics and energy concerns
should be considered.
                               204

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     Section  169A(a)(l)  sets  out  the basic  objective  of the
visibility program:
     Congress hereby declares as a national goal the pre-
     vention of any future and the remedying of any exist-
     ing, impairment of visibility in mandatory Class I
     Federal areas which impairment results from manmade
     air pollution.
     While visibility is an aesthetic value which is reversible,
Congress added the visibility  program to the Act because it was
concerned with  impairment  of scenic vistas  that  are enjoyed by
many people  and the economic harm  that  would  befall localities
dependent on revenues from  these people  if they were  to  stop
visting  these  areas  because of  impaired  visibility or degraded
vistas.  As the House Report explained:
     Certain areas of the United States depend upon their
     intrinsic beauty and historical and archeological
     treasures as a means of promoting their economic
     viability.16
     Congress was  aware  of the  potential  costs  associated  with
the visibility program it  mandated,  and included several provi-
sions  to minimize the costs of  the program,  as  the House  Com-
mittee explained  on  pages  206-207  of its Report.   EPA's final
visibility  regulations  fully  implement  these  provisions  to
minimize cost,  and EPA has no discretion  simply  to ignore  Con-
gress '  mandate  because  of some  general  speculation regarding a
comparison  of the  costs  versus the  benefits of  the  program.
Moreover, EPA's phased approach  further  minimizes the potential
cost of  the program in recognition  of scientific and technical
limitations.  EPA  is  now in the process  of  developing guidance
on  assessing the benefits  of good visibility.   A "Visibility
Benefits Workbook" will be made  available for public review and
comment when it is available.
     Several  comments  were  also presented  regarding the  con-
sideration of  cost in making  the reasonable attribution demon-
stration for identifying sources which would be subject to BART.
16HR Rep.  No.  95-294, 95th  Congress,  1st Sess.  203.04 (1977).
                              205

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A  few comments  indicated that  EPA had completely  ignored the
cost-benefit analysis  for BART.   EPA believes that the determi-
nation of  whether a source  impairs visibility is clearly inde-
pendent of the cost to the source of remedying any impairment it
causes.  Once  a  source is determined to cause the impairment of
visibility, cost and other nonair quality considerations can and
are taken into consideration in  determining the level of control
which represents BART, as the BART  guidelines provide.
      The rest of this  section responds to  the twenty-two com-
ments on the  "Preliminary Assessment of Economic  Impact of Visi-
bility Regulations"  EPA released with its proposal.  This docu-
ment  has been revised  in  response to comments  and changes in the
final regulations.
      The  shortcomings of  the  analysis  attributed to the use of
screening  curves were  pointed  out in 14 of the 22 comments.  The
chief concern centered around the  use  of curves  derived  from an
unvalidated model.   Specific objections were  made to the use of
simplifying assumptions  to derive the curves,  such as:
      0  A  "representative" 1,000 Mw powerplant,
      0  Uniform terrain,
      0  Worst case meteorology,
      0  Fixed observer-plume-sun geometry,
      0   Site-insensitive chemical transport estimates,
      0  Negligible impairment impact for certain chemical  reac-
         tions , and
      0  Gaussian  plume  dispersion  modeling  (appropriate  for
         short transport distances)  for all distances.
      Four  respondents  objected to  the preliminary  assessment's
 application of screening curves intended  for distances of up to
 100  km to plants  located  beyond   that  distance.    One  comment
 labeled the  use  of the  same  screening  curves  for  eastern and
 western sites as inappropriate, given the  influence of climate
 and  terrain on the screening results.
                               206

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     ERT, which developed  the  screening curves,  objected to the
use of the curves for identifying specific sources.  ERT claimed
that  the curves were  intended  to  be  used  only as a  means  to
estimate generically the numbers and types of industrial sources
having potential visibility impact.
     EPA agrees that the screening curves have shortcomings, but
these limitations of the screening curves were and will continue
to be recognized.    For  example, ERT  contends  that the curves
were not meant for identifying single sources for mandatory BART
retrofits.  They were not so used.  The curves were only used to
establish  a  universe of  sources potentially affected  by visi-
bility regulations.  That universe is identified for EPA as part
of the documentation of the methodology, assumption, and results
of the  analysis.  At  no  time does the  preliminary assessment
allege that  the analysis or the ERT screening  curves  portray a
precise  indication of the  true visibility  impacts  at specific
facilities.   As noted in  the  preliminary assessment,  EPA be-
lieves that  such  a  determination can  only  be  made on  a site-
specific basis using analytical and modeling tools deemed appro-
priate by the facility in question.
   '   In  essence, the analysis  in the preliminary assessment was
never intended to be site specific.   The only reason, for includ-
ing the  names of individual sources was  to  provide an opportu-
nity  for the findings to be carefully reviewed by the interested
parties.
     EPA  attempted  to  minimize the  problems   associated  with
using the curves  as the  sole screening device by using other
criteria as well.  No undue importance was placed on the results
of either screening method.   The  assessment  emphasizes rather
than  ignores the need for site-specific analysis prior to estab-
lishing  a final list  of  sources requiring controls  for visi-
bility protection.
      The  one comment concerning the use  of  "the same screening
curves  for eastern and western sites" overlooks  the  fact that
different  curves  were  used  to screen  the  sources located  in
                              207

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different regions.   The screening curves  used assume different
wind velocity  and direction, mixing  height,  relative humidity,
and visual range constraints for each of nine regions.
     Several respondents  asserted that the  results  of the ana-
lysis  were  rendered  useless by  the  reliance  on inappropriate
assumptions;  A  summary of the comments made on each assumption
is presented along with a response.
Comment;   Eight comments  cited  the  National  Emissions  Data
System (NEDS)  as a poor  data  source,  notorious for being inac-
curate,  incomplete,  and  out  of date.   One  commenter blamed
specific incorrect NEDS entries  for the preliminary  assessment's
overstatement  of visibility impacts  caused by the Bullock  and
Hayden plants.
     Other  comments  voiced concern that screening  from the base
of sources  included  in NEDS underestimated the number of sources
potentially affected.  NERA,  the American Paper Institute,  and
the National   Forest  Products  Association  pointed  out that
sources  whose emissions  are not reported in NEDS,  because they
commenced  operation after  the  data  were initially  collected,
were not included in the preliminary assessment.  Other sources
whose process   emissions  are  compounded  by  fugitive  emissions
 were  also missed by the  assessment.   Since the regulations will
 apply to all sources with the potential to emit up to 250 tons
 per year, the American Petroleum Institute  feels that screening
 based on  actual emissions  underestimates the number of sources
 likely to  be  affected.  (UARG  feels that the inclusion of only
 powerplants in  the   analysis is  evidence  that not  all potential
 sources have been considered.)
 Response;   The NEDS data base  was  used because  the  data con-
 tained therein  (source inventories by  category, estimated annual
 emissions,  calculated  distances to  Class  I  areas) made it a
 reasonable  choice for a preliminary analysts.   Chapter  6 of the
 assessment  presents a thorough evaluation  of the  NEDS  data and
 its  shortcomings,   and notes  the uncertainties  in the  analysis
                                208

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arising  from  its use.  The  conclusion after extensive checking
of  individual  entries is similar to that  expressed in the com-
ments; i.e.,  that an  analysis based  on possible overstatements
of  emissions  will  possibly  result in  an overestimate  of  the
number of sources  likely  to  be affected by the visibility regu-
lations.   This conservative bias was intentional.
     Further,  for  all the final  sources selected as potentially
being  impacted  by visibility regulations  (which turned  out to
include  only  utility  powerplants),  estimates of  current emis-
sions  from  each utility's  latest submissions  to  the  Federal
Energy Regulatory Commission (FERC Form  67) was  specifically
obtained.  This  was  done  explicitly because of concerns regard-
ing the  currency and accuracy of the  NEDS  data.   In some cases
this  was further  augmented  by  discussions  with utility offi-
cials.  When utility emissions reported on FERC Form 67 differed
from  those  calculated using AP-42 formulas on the  FERC  Form 67
fuel data, the calculated estimates were used.  This may explain
why the Colorado-Ute estimates of NO  emissions are different at
                                    X
the Hayden powerplant.
     Omissions from  the NEDS data  base resulting  in  an under-
statement of  the possible impacts of  any  regulation can occur.
However,  evaluation  of successive  NEDS printouts indicated that
additions of new sources of emissions were generally included in
the data base, such that some effort had been made to update the
NEDS.   Unfortunately,   the  NEDS data  base  is  the  only  source
readily  available  which provides the  type  of data  necessary to
perform the analysis  described  in  the assessment report.  What-
ever the omissions from the  NEDS data, the relative impacts and
the conclusions  of  the preliminary analysis would not  likely
change.  The analysis  performed  was to provide an initial indi-
cation of the likely impacts of the visibility regulations.  The
analysis was  not to provide  a complete and accurate assessment
of  all sources  which eventually could  be  affected  by  the visi-
bility regulations.
                              209

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     The  fact  that only  utility  powerplants  were  identified
should not  necessarily be construed  as  an indication  that all
sources  have  not  been  identified.   Many  of  the  industrial
sources  were exempted from  consideration because of  specific
provisions  in the Clean Air  Act.   According  to  the legislative
record,  these provisions were  explicitly  provided to focus the
BART regulations on a  few large powerplants,  especially those in
the West.   Hence,  it is not  surprising that when the exemptions
were  applied  to  large  industrial and  utility  sources,  only
utility  powerplants  remained  identified in the analysis  as
potentially being affected by the BART regulations.
Comment:  Both sources of equipment  cost estimates used in the
analysis  were  criticized by Salt River Project (SRP).   Cost
estimates prepared by  Pullman Kellogg have only been  issued in a
draft  report and hence are   subject to  change  before the  final
report is published.   SRP  feels that only  final estimates are
acceptable  input  for  an analysis  to  support rulemaking.   Fur-
thermore,   SRP  doubts   that   costs  used  in  an  NSPS  evaluation
(i.e.,  for  new sources) are appropriate  for retrofitting con-
trols  to existing equipment.   (See  additional discussion of cost
estimates below.)
Response;   Cost estimates for  control equipment  were explicitly
stated to  be  average unit  costs for  "model  plants."   While
assessments by other  parties  (including NERA) have  found  these
costs  to be generally  reasonable,  the estimates  are just average
costs.  The specific  costs of  installation  at any given source,
particularly in a retrofit situation,  can differ,  potentially by
 substantial  amounts   from  the  estimates  provided.   The costs,
however, were chosen to be on the whole conservative  (high).  An
 explicit add-on penalty reflecting almost a  50  percent increase
 in the  capital costs  for any  scrubbers  retrofitted  for meeting
 visibility  regulations  was   incorporated  into  the  analysis.
Hence,  the  retrofit   scrubber costs  for powerplants  was not
 solely based on  the costs  for  putting scrubbers on a new power-
 plant.
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     Chapter  6  of  the  assessment  addresses  this issue,  and
stresses that  cost estimates for NO   control  equipment in par-
                                    X
ticular  are  especially  uncertain.    Given  the  nature of  the
analysis, and  the  expectation  that site-specific analyses would
be the part  of any final rulemaking affecting specific sources,
the average  costs  were deemed appropriate estimates  for a pre-
liminary assessment.
Comment;   Atlantic  City  Electric  challenged the  use  of coal
prices from  the  IGF Coal  and Electric Utilities Model for esti-
mating the  cost of  control  via  conversion to  low-sulfur  coal.
Atlantic City  Electric claims  to be facing substantially higher
prices than  estimated  for  the  analysis because the availability
of coal with low sulfur and an ash-fusion temperature low enough
for a cyclone boiler is quite limited.
Response;   Estimates  of  coal   prices  from  the  ICF   Coal  and
Electric Utilities  Model  (CEUM)  are subject to the same sort of
site-specific  considerations  as mentioned  above  for  control
equipment.   The CEUM price estimates do account for variation in
sulfur  content,  heat  content,  and volatility  among  coal  re-
serves.  Prices for coals to satisfy demand constrained by other
requirements,  such as  low-sulfur combined with a  need for  low
ash-fusion temperatures with limited  coal reserves could poten-
tially result  in higher  coal prices than projected by the CEUM.
Such  an  adjustment would  be warranted in a  more detailed ana-
lysis of specific compliance options at individual plants.
Comment:   One data  source not  used  in  the  analysis  but con-
sidered  important  by  five respondents  is  the  list  of sources
compiled by  the Federal  Land Managers  (FLM).   Four of the com-
ments  indicated  that the  assessment was  incomplete  without
consideration  of the FLM's evaluations; one objected to the use
of calculations of  impairment rather than observations of impact
to support visibility regulations.
Response;   With  few  exceptions  the  sources   responsible  for
visibility  impairment  according to the FLM  are included in the
                              211

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NEDS data base and have therefore been screened according to the
assumptions used in  this  analysis.   The sources compiled by the
FLM serve as another approach to identifying sources potentially
impacted by visibility  regulations  and are based on a different
set of  selection  criteria than used in the assessment.  The two
efforts serve  to  compliment one another rather than being mutu-
ally exclusive.
Comment;  Five comments questioned the preliminary assessment's
interpretation of BART as  other than NSPS,  finding  it in con-
flict  with  EPA's  "Proposed  Guidelines  for Determining  Best
Available  Control  Technology  for  Coal-Fired Powerplants  and
Other Major Stationary  Sources  (Draft)."
Response:  BART for  the purpose of  the  assessment was  defined as
that  technology necessary  to  roll back  emissions  to meet the
assumed threshold values.  The BART guideline document proposes
that  BART emission  limits  selected by the states that are less
stringent than the NSPS  limits  must  be justified.  However,
limits  less stringent  than NSPS are not  prohibited.  (See Sec-
tion  4.9.4  for further  discussion of BART  guidelines.)
Comment;   Four comments   addressed  the  visibility  impairment
thresholds  used in  the analysis.  Pacific  Power and Light  and
Colorado-Ute  Association considered the selection  of the thres-
hold levels somewhat  arbitrary, noting that the  interpretation
of  "perceptible   impairment"   is   the  subject  of  considerable
debate.  TRC  and the Utility  Air Regulatory Group (UARG) objec-
ted  to the  adjustment  of the threshold levels without  "suf-
 ficient" analytical justification.
Response;  Aware  of   the  controversy  surrounding attempts  to
 define  "perceptible impairment,"  EPA selected  two  threshold
values each for discoloration and visual range reduction to test
 for sensitivity  of the  results  to different assumed levels  of
 impairment.   In  the  draft report,  it was  clearly  noted  that
 defining these threshold limits was critical and subject to many
 considerations.
                               212

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Comment:   Five comments  contained  objections  to screening based
on  distances  calculated  from  the source  to  the centroid  of a
Class  I  area.   All of the objections  stemmed from  concern that
using  this  assumption  underestimated  the   number  of  sources
potentially influencing  the Class  I  areas.   Some  comments ad-
dressed the possibility  that a source might have an effect on a
large  Class  I  area without affecting  the  centroid;  others were
concerned that protection of the Class I area's integral vistas
was  not  assured  by  screening for protection  of  the  centroid
only.
Response;  EPA shares  the concern expressed over the proper use
of  the proposed distance criteria and the appropriate selection
of  the fixed centroid in each  Class I area.   These concerns are
discussed  in  Chapter  6  of  the  assessment.   The  inclusion  of
alternative screening  criteria which  did  not rely on  the dis-
tance  criteria  was  intended  to mitigate  some of  the  problems
associated  with   centroid-to-centroid  distance  calculations.
Comment:   Salt River  Project objected to the generalized use of
a 12.5 percent  capital  charge rate.   SRP pointed  out  that the
rate is very sensitive to utility financing practices as well as
the underlying cost of money,  and noted that a 12.5 percent rate
is  in the low range for specific western utilities.
Response:   Consideration of individual  methods of  utility fi-
nancing  was beyond  the   scope  of a preliminary  analysis.   The
capital  charge  rate  chosen  was  therefore not purported  to  be
representative  for any specific utility.   Further,  the capital
charge rate used in the  analysis  was  chosen  to be conservative
(high),  and was based on utility  financing costs  for a private
utility  identified  by  the  Electric  Power  Research Institute
(EPRI).  Note that the capital charge  rate of 12.5 percent  is in
real  terms and is  much lower  than   the  corresponding capital
charge rate in  nominal terms,  which is on the order of 18  to 19
percent.   Since  all the  associated  capital  costs  were  in real
1980  dollars  the correct charge rate  to use  for the assessment
                              213

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is a real  capital  charge rate.  For municipal and quasi-govern-
ment utilities (TVA, Bonneville, and SRP), the utility financing
costs would be lower than that used  in the assessment.   There-
fore, the  capital costs on an annualized basis  included in the
assessment would be overstating the costs to these public utili-
ties.   To  be  conservative  (i.e.,  a  bias toward overestimating
the  costs), only  the capital charge  rate  for privately-owned
utilities was  used.
     The following comments concern issues which the respondents
consider  an  essential  part  of an  economic  assessment of the
proposed regulations,  but which were  not -addressed.
Comment;   Six comments  expressed concern that the methodology
understated the potential  impact of visibility regulations  by
ignoring  any  additional costs associated with protecting  inte-
gral vistas as well as the  specific  Class I  areas.
Response:   The  criteria outlined  for the  assessment  specified
the use of distances  calculated to  the Class I  area's  centroid.
Chapter 6  of  the assessment  questions the  appropriate  applica-
tion of the  distance criteria when  considering  important  inte-
gral vistas.   However, since the issues associated with integral
vistas, (i.e., whether  these  were  to be incorporated into  visi-
bility regulations at all  and how they were to be defined) were
 not resolved  when the analysis was  done, explicit consideration
 of such vistas was not  incorporated into the preliminary assess-
 ment.  Under the  final  regulations,  the State may consider cost,
 energy and other  relevant factors in determining the appropriate
 degree of protection  for integral vistas.
 Comment:   Nine  of the  22  comments critized  the  assessment for
 failing to include  an estimate of  the benefits  to  be derived
 from  visibility  regulations.   Some of  the comments challenged
 the  ability  of  the  proposed  regulations  to  produce benefits
 warranting the   expenditure   of  millions  of  dollars;,,  others
 claimed that  Congressional appropriations already expressed the
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taxpayers  (low)  valuation of aesthetic  worth.   All of  the  re-
spondents  felt  that a benefits assessment was  necessary to  put
the cost assessment into perspective.
Response;   EPA  agrees  with  the  importance  of assessing  the
benefits to be produced by any visibility regulations.   Page 1-3
of the  Introduction and Executive  Summary stresses this impor-
tance and points out that visibility impairment causes  different
levels  of concern  for different  Class  I  areas.  However,  no
overall benefit  assessment has been performed  due  to  the case-
by-case nature  of the visibility program.  As  noted earlier in
this  section,  benefit analyses will be made on  a  case-by-case
basis as part of the BART demonstration.
Comment;   The  assessment  understated  the  costs  of  imposing
visibility regulations, according to three comments, because no
secondary  or tertiary  economic impacts were  analyzed.   Among
those potentially  affected are fuel suppliers,  ratepayers,  tax
payers supporting  additional  administrative  staffs, and indus-
tries forced to relocate or reconsider expansion plans.
Response;  The preliminary assessment does not consider economic
impacts  beyond the estimated  capital  and annualized  costs  for
utilities  identified  for  control,  and  the  influence  of these
costs  on  utility  electricity  rates.   The additional economic
impacts associated with control of a particular source  should be
addressed  in the site-specific analyses that  will  be  conducted
as part of the regulatory requirements.
Comment;  Three respondents found the assessment to be  deficient
because no economic analysis was prepared to support development
of each  state's  long-term strategy for protecting visibility in
Class I areas.
Response;  The  report is  explicit  in stating that this analysis
was prepared to support the initial regulations, which deal with
near-field impairment that can be  traced to  a single existing
source  or group of sources.   Other considerations  with respect
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to visibility  impairment,  such as control of  regional  haze and
any  long-term  strategies  potentially  to  be  imposed by  state
agencies were beyond the scope of this assessment.
Comment:   Three  comments  cited  the omission of  any  analysis
supporting new source reviews  as  a shortcoming  of the assess-
ment.
Response;  The focus  of the assessment was an economic analysis
of  the costs  for major  existing stationary  sources  to comply
with visibility  regulations.   Analysis  to  support  new source
reviews was not conducted as the cost is associated with the PSD
program.   The preamble  to  the regulations  discusses  the  anti-
cipated affects of the  final regulations on new sources.
Comment:   Three of  the comments  questioned  the usefulness of
ICF's  findings because  no  other  factors  contributing to  visi-
bility impairment were considered.  A  fourth  respondent came to
a similar conclusion because  of the omission of any considera-
tion of regional  haze.
Response:   The  assessment  was prepared  to  support near-field
impairment that  can be  traced to  a  single  existing source or
group  of  sources.   Hence,  the  influence  of   other  pollution
 sources to the extent  that these  sources contribute to regional
haze  problems were not  considered.   To  the  extent that  these
 other sources affect the overall  general background visibility
 levels,  this  effect to  a  certain degree was included in the ERT
 screening curves which account for regional  variations in humid-
 ity,  background  visibility,   windspeed,  stability,  and  other
 meteorological conditions.
 Comment:   Twelve of  the  comments  submitted  included evaluations
 of  the  estimates of the costs of installing  controls  or initi-
 ating  other  control  strategies.   Eleven  of   the  evaluations
 considered the  estimates to be an understatement of the actual
 potential  costs,  due  primarily  to   the use of inappropriate
 assumptions (see  discussion above).  One evaluation labeled the
 costs as overestimates.
                                216

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Response:   The  cost  considerations  specific  to  each  source
assure  that any  estimate based  on  average unit costs  in many
instances could be  wrong; some plants will be' able to comply at
lower  costs and  others  at  higher costs.  However,  on average
these  costs, are likely to be  representative  of  the total costs
incurred.
Comment;  Eleven  respondents  concluded that one or more sources
had been screened incorrectly.   Most  of the  comments concerned
sources  which  had been named  as  possible contributors to visi-
bility  impairment.   The  objection was  raised that  inclusion in
such a  list of "offenders" forced the source to prove its inno-
cence.   Respondents  who  felt that their sources had been missed
seemed  somewhat  concerned about  the  possibility  of incurring
costs  at some  later date, but primarily made the  argument that
missing  sources  led to an underestimate of the  potential costs
being assessed by EPA.
     VEPCO  pointed   out   specifically  that Mt.  Storm had  been
included  in the  analysis incorrectly because  of  an error  in
recording  the  initial  date  of  operation  for one  of  their
boilers.  VEPCO  also stated that  the  distances  to  the affected
Class I areas from Mt. Storm are wrong.
Response:  The report  emphasizes  that  those sources referred to
as potentially affected by visibility regulations are identified
only for the purposes of this analysis.  The data sources and
assumptions  used  determined the  outcome of the screening  pro-
cess.    Although  every  effort was made to  minimize the :bias
created by  the  input assumptions,  the  uncertainties and limita-
tions of the analysis were  acknowledged in the first pages  of
the report.
     Concerning the initial date of operation for the third unit
at the  Mt.  Storm plant,  the assessment stands  corrected.   The
initial  date of operation for this unit was  that identified  by
the. Department of  Energy in  its Inventory  of Powerplant  and
Industrial  Powerplants.   Note  that in  correcting for this  date
                              217

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of operation, the estimated impacts at Mt. Storm would be higher
than indicated in the assessment.  This is because the emissions
from the  third unit,  having been exempted due  to  its age,  were
not included in the assessment.  Failing to include this unit in
the cost  estimates  understates both the estimates of visibility
impairment  and  the 'costs  for complying  with the  visibility
regulations.
     The  distance  calculations are -taken from NEDS  (not calcu-
lated  from the accompanying map) and may be either (a) mislead-
ing, due  to the use  of centroid  to  centroid distances, or (b)
wrong.  Any future  analysis  regarding  Mt.  Storm  will double-
check  the distance to the  Class  I area.
Comment;   The  assessment  of  the  possible or  probable control
strategies was incorrect in at least  three instances:
     0 Atlantic  City  Electric claimed that  the use of low-
        sulfur coal  was   at best  very  expensive  and  at worst
        impossible  because of the  limited availability  of
        low-sulfur, low-ash fusion coals.
     0 Jacksonville  Electric  claimed that  their current fuel
        supplies  for  the  Northside  plant contain  1.8 percent
        sulfur, not 1.4 percent, which  makes  the  assumed  "cost-
        less"  switch to 1.3  percent  sulfur oil a  very  expensive
        strategy.
      0 Salt River Project claimed that the retrofit  of NOx con-
        trol  equipment postulated by ICF  was either  much more
        expensive  than indicated or impossible when the existing
        equipment   is  incompatible  with the  equipment used  to
        develop the cost estimates.
 Response:   Atlantic  City Electric — As mentioned  previously,
 site-specific considerations such as the requirement  for low-ash
 fusion,  low-sulfur coal is an important consideration and could
 result in higher low-sulfur coal prices than used in the assess-
 ment.   EPA  recognizes  that  there  are limited coal  reserves  of
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low-sulfur, low-ash fusion temperature coals and that the avail-
ability and  likely costs of this  coal  for specific powerplants
needs to be evaluated on a case-by-case basis.
     Jacksonville  Electric — DOE's   Cost and Quality of Fuels
for Electric Utility Plants - 1979,   which  is  prepared   from
utility submissions,  lists  the sulfur  content of  oil delivered
to the Northside plant as 1.42 percent.
     Salt  River  Project — Chapter 6 of  the assessment acknow-
ledges that there  is  uncertainty  inherent in the cost estimates
for NO  controls used in the analysis and that there is a debate
      X
about the  applicability of specific  NO  retrofit  equipment for
                                        2\.
specific boilers.  Further, assessments of the technical feasi-
bility of different options were not considered to be within the
scope of the assessment.
Comment:   Two  respondents claimed that the estimates  of  visi-
bility  impairment  presented  in  Chapters  One  and  Two  disagree
with those presented in Chapter Three.
Response:   The  estimates  of visibility  impairment  shown  in
Chapter Three are the correct estimates.  The derivation of each
estimate is presented in detail in the  later sections of Chapter
Three.  The  differences between the  estimates shown in Chapter
Three and  those  presented in Chapter Two .arise because the more
detailed  calculations in  Chapter  Three  take  into  account (1)
adjustments  to  represent average  daily emission;  (2)  planned
improvements  in pollution  control equipment;  and (3)  intended
changes in fuel purchases.
Comment:   Pacific  Power  and  Light questioned   the  estimated
impacts of the  Centralia plant on the  Mt. Rainier Class I area.
Their analysis  of the  assumed  meteorological conditions,  plume
behavior,  and  elevation of the Class I area indicated that the
impacts are more likely to be inconsequential.
Response;   The estimated  impacts  of the Centralia  plant were
                                                 !••'
derived based  on the screening curves,  and rely on the assump-
tions  about meteorology  and plume  behavior  that were  used to

                              219

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develop the curves.  As mentioned in the preceding discussion of
the  screening  curves, terrain  was  not considered  in preparing
the curves.  The problems associated with inaccurate meteorolog-
ical assumptions  and with excluding  terrain  are highlighted by
examples  such  as  the  Centralia/Mt.  Rainier  case.   Adequate
consideration  of these  site-specific conditions should  be in-
cluded  in  future analysis  as  part  of  a specific  regulatory
action or determination.
Comment:  Colorado-Ute Electric Association took issue with the
visibility  impairment attributed  to nitrogen oxides  (NOx) emis-
sions  from the  Hayden plant.  Colorado-Ute  concluded that the
estimates  overstated actual  emissions of  nitrogen oxides from
the  Hayden  plant  two-fold,
Response;   The NOX  estimates  for  the Hayden  plant which were
challenged  by  Colorado-Ute were calculated  using AP-42 formulas.
EPA  acknowledges that  the  formulas  may overstate emissions
somewhat because there is no adjustment  included for tangential
firing.   Such  a consideration should be  included in any more
detailed site-specific  analysis.   Nonetheless,  the emissions
estimated from Hayden!s  one  tangentially-fired unit  would only
be about 25 percent lower than  the  estimate made  assuming front-
firing using  general NOx  emissions  data  often used for such
powerplants.   The perceived  overstatement can more  reasonably  be
attributed to  a  misinterpretation of  the estimates.   Maximum
daily  emissions  rates  (that is  100%  output  for 24  hours) were
calculated, not  an  average  annual or  average daily rate.   By
using  1979 fuel  data,  average  daily emissions  rate is  about
one-half the  maximum daily  rate shown  in the report.   This  is
approximately the current rate  suggested by Colorado-Ute.

4 12  IDENTIFICATION UNDER SECTION 169A(a)(2) OF MANDATORY CLASS
       I  FEDERAL AREAS IN WHICH  VISIBILITY IS  AN IMPORTANT VALUE
     The Utility Air Regulatory Group  (UARG)  and  a few other
commenters  complained  that  the  Administrator's  November 30,
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1979, identification of mandatory Class I Federal areas in which
visibility  is  an important  value  under Section  169A(a)(2)17
merely "rubber-stamped" the recommendations  of the Secretary of
the  Interior.   UARG,  while  recognizing that  this  action  was
"final," requested EPA to acknowledge that "the existing list of
Visibility Areas  .  .  .  be reduced as appropriate, when facts so
justifying are brought to the Administrator's attention."
     As  EPA noted  in  the  preamble  to  the November 30,  1979,
notice,  the  Administrator will revise the list  on  the basis of
new,  information.   44 Federal  Register 69123,  col.  3.  Revision
to the  final list promulgated November  30,  1979,  is explicitly
provided for in Section  169A(a)(2)  itself  ("From  time  to time
the  Secretary of  the Interior may revise such identifications")
and  the Act's  Conference  Report  ("The  Administrator  and  the
Secretary of Interior may update the applicable recommendations
and  list periodically  when  appropriate").  H.  Rep.  No.  95-564,
95th Cong.,  1st Sess.,  155  (1977).  Thus any person who desires
on the basis of new information to have the Administrator revise
the  list should administratively  petition the  Secretary of the
Interior to recommend  any  such revision to the Administrator.
     The several  non-UARG  commenters on this  point  seemed to
imply that  somehow  the  November 30,  1979, action could still be
judicially challenged, either  as part of a judicial challenge to
the  final regulations under § 169A(a)(4) for visibility protec-
tion  or otherwise.  This is   patently wrong.   The November 30,
1979, action was  final  action, clearly identified as such, that
amended  40  CFR Part 81.  Under Section  307(b)(l),  any petition
for  reivew   had  to  be  filed  within 60  days  after November 30,
1979.   Indeed,  one  such  petition was timely  filed challenging
17
  44 Federal Register 69122.
                              221

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one of  the identifications and EPA raised no  argument that the
complained-of action was not final.18
     Although EPA stated in its notice of the proposed list that
it would consider no substantive issue relating to the list ripe
for  judicial  review  until  the  § 169A(a)(4)  regulations  are
promulgated "since the effect of the identifications will remain
largely  uncertain until then,"  EPA abandoned this  position in
its notice of  the final  list.   In  the preamble to  the final
list,  which throughout  referred to  the action  as  "final" and
termed  the list a  "promulgation,"  the Administrator explicitly
rejected  the  request of one  commenter that  promulgation of the
final  list be postponed so that  it could be addressed together
with  the  regulations  proposed  under Section  169(A)(a)(4) for
protection of visibility.  The Administrator explained:
      [S]uch an  approach  [deferring promulgation of the
      final list] would be  contrary to  the congressional
      scheme—clearly set out  in section  169A—of  promul-
      gating the list of areas in  advance even  of  the
      report to  Congress containing the technical  outline
      for  the eventual visibility  regulations.  44 Federal
      Register 69123, col.  3.
The Administrator noted that the economic effect of the  regula-
tions under §  169A(a)(4)  cannot  be evaluated until those  regu-
lations are proposed  and promulgated,  a  time Congress  contem-
plated would be  after  the final list under Section  169A(a)(2)
was promulgated.   44 Federal  Register 69123,  col. 2.
      Thus  the  list  promulgated  under  Section  169A(a)(2)  on
November 30,  1979, was final Agency  action,  as UARG recognized,
and  under Section 307(b)(l)  the time for filing a petition for
review of the  list has   long  since  expired.  Any  person  may,
 18See Chevron U.S.A.,  Inc.  v.  EPA,  5th Cir.,  No.  80-3081.   Peti-
   tioners in this case also filed an administrative petition for
   reconsideration which EPA denied on October 3,  1980, 45 Fed.
   Reg. 65585.  This notice, together  with the preamble to EPA's
   November 30, 1979,  final list of areas,  answers completely the
   substantive  and procedural  objections  raised  by the  above-
   noted commenters in the present rulemaking.
                               222

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however, administratively petition the Secretary of the Interior
to recommend to the Administrator that he revise the list.

4.13  MISCELLANEOUS
     Nonferrous  Smelter  Orders  -  There  were five  comments re-
ceived  concerning  the  control  of  emissions  from  nonferrous
smelters  in the  Southwest.   At  least two of  these commenters
suggested  inclusion of  some requirement to reduce visibility
impairment  in a  Nonferrous  Smelter  Order  (NSO)  [Section 119],
while others  said a smelter  with an  NSO should  be exempt from
any  visibility  requirement.    Section  119  of  the Act  allows
certain smelters that cannot afford the constant controls neces-
sary  to attain and maintain the  SO2 NAAQS to use supplementary
control  systems  on an  interim basis.   The  NSO  program under
Section 119 simply does  not concern requirements for protection
of visibility.
     Reversibility  of  Visibility  Impairment  -   There   were  a
number  of comments  which brought up  the  fact that visibility
impairment  is  a reversible phenomenon.  Certain commenters also
suggested  delaying the  final promulgation of these regulations
since visibility  impairment does not affect health or welfare of
individuals.   In  fact,  visibility  is  a "welfare"  affect and
there is  no basis in law  for EPA  to ignore Congress' mandate to
promulgate  these  regulations.   The Agency agrees that visibility
impairment  is  a  reversible  phenomenon;  however,  Congress was
aware  of this  fact and nevertheless  it established a two-year
deadline   for  promulgating  these  regulations.   This and the
legislative history   indicate   the  great importance  Congress
placed  on protecting visibility.
      Several  commenters raised  concerns over the apparent dis-
crepancies  between the "in existence"  definition  in  the proposed
regulations for visibility and the "in  existence"  definition in
the proposed  regulations for  stack heights.
                               223

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     For the purposes of the visibility regulations in existence
     "means that the owner or operator has obtained all
     necessary preconstruction approvals or permits re-
     quired by Federal, State, or local air pollution emis-
     sions and air quality laws or regulations and either
     has (i) begun, or caused to begin a continuous program
     of physical on-site construction of the facility or
     (ii) entered into binding agreements or contractual
     obligations, which cannot be cancelled or modified
     without substantial loss to the owner or operator, to
     undertake a program of construction of the facility
     to be completed in a reasonable time."
     The proposed stack  height regulations  on  the  other  hand
define "in existence" as meaning "that stack height (of a stack)
which has  been constructed,"  and  the commenters  felt  that "in
existence" under  § 169A  should connote "complete construction."
     The 1977  Amendments employed two  concepts  to describe the
status  of  source  construction:   facilities or  source  on which
construction had "commenced" and facilities "in existence."  The
phrase "in existence" is used in provisions dealing with PSD and
visibility, as well as stack height.
     For visibility  protection, Section  169A(b)(2)(A) mandates
an  SIP  requirement that each  major  stationary source "in exis-
tence" on the date of enactment of the Amendments, but which has
not  been in operation for more than fifteen years  as  of that
date, must apply BART.   In contrast to the  provisions dealing
with "in existence"  Section 169(a)(2),  a source which has "com-
menced  construction"  for PSD  means  a source  that has obtained
all necessary preconstruction permits and either begun physical
on-site construction or entered into binding contractural agree-
ments which cannot be  cancelled without substantial loss to the
source.
     Since the  1977  amendments defined commence construction to
include  the acquisition of  permits,  the  beginning  of actual
construction, etc.,  arguably  "in existence" must mean more, and
in  fact  for  the purposes of Section 123 "in existence" has been
taken to mean physically constructed.
                              224

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     Congress,  however,   stated  repeatedly that  the  PSD  and
visibility programs should be harmonized to the extent possible.
The effect  of EPA's definition of "in existence"  is  to assure,
as Congress  intended,  that a major source  be  subject either to
BART  under  § 169A  as  an  existing  source, or  to  PSD  as  a new
source.   No  commenter challenged this  reasoning which EPA set
out with its proposal.   Under one commenter's  approach,  those
sources  which  had commenced  construction prior  to  August 7,
1977,  but which were not physically "in existence"  on that date,
would not be  subject  to  either the BART or the PSD requirement.
As noted, the Agency believes that a source either is new (i.e.,
subject to PSD) or existing (subject to BART)  and that  it cannot
be neither:   therefore,   sufficient  reason exists  for defining
"in   existence"   differently   for visibility   than  for  stack
heights.  An  additional  reason  for  this difference  is that in
the stack height definition "in existence" was proposed in order
to credit sources  which  raised their stacks or constructed tall
stacks  prior  to December 31, 1970,  such  that  they would not be
subject  to more retroactive requirements.  However, BART by de-
finition is retroactive.
                              225

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                                   TECHNICAL REPORT DATA     .
                            (Please read Instructions on the reverse before completing)
 REPORT NO.
 EPA 450/2-80-083a
 TITLE AND SUBTITLE                                      -
 Summary of Comments and  Responses on  the May 22,  1980
 Proposed Regulations  for Visibility Protection for
 Federal  Class I Areas
            6. PERFORMING ORGANIZATION CODE
                                                              REC
                                                                  'lENT'S
              REPORT DATE
               October 1980
 AUTHORCS)
                                                            8. PER
 PERFORMING ORGANIZATION NAME AND ADDRESS

 PEDCo  Environmental,  Inc.
 11499  Chester Rd.
 Cincinnati, Ohio   45246
                                                             10. PROGRAM ELEMENT NO.
             11. CONTRACT/GRANT NO.

                  68-02-3512
2. SPONSORING AGENCY NAME AND ADDRESS
                                                             13. TYPE OF REPORT AND PERIO1
 Office of Air Quality Planning  and Standards
 U.S.  Environmental  Protection Agency
 Research Triangle Park, N.C.  27711
                 PE.OF R
                  Final
             14. SPONSORING AGENCY CODE
5. SUPPLEMENTARY NOTES
 6« ABSTRACT


  This report  summarizes the  comments received on the proposed Visibility Regulations
  and accompanying guidelines by major issue.   It also  provides discussion of EPA s
  position on  these issues and subsequent  changes to the  final rules.
17.
                                 KEY WORDS AND DOCUMENT ANALYSIS
                  DESCRIPTORS
                                                b.lDENTIFIERS/OPEN ENDED TERMS
                                                                           c.  COSATI Field/Group
  Response to comments
  Visibility
 Public Comments
 Visibility
18. DISTRIBUTION STATEMENT
  Release to public
19. SECURITY CLASS (This Report)
   Unclassified
21. NO. OF PAGES
  225
2O. SECURITY CLASS jTMs page)
                            22. PRICE
EPA Form 2220-1 (Rev. 4-77)   PREVIOUS EDITION is OBSOLETE

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