Determination of Attainment of Ozone Standard, St. Louis Area; Approval and Promulgation of Implementation Plans, and Redesignation of Areas for Air Quality Planning Purposes, State of Missouri

Note: EPA no longer updates this information, but it may be useful as a reference or resource.

[Federal Register: May 12, 2003 (Volume 68, Number 91)]
[Rules and Regulations]
[Page 25418-25442]
From the Federal Register Online via GPO Access [wais.access.gpo.gov]
[DOCID:fr12my03-10]

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ENVIRONMENTAL PROTECTION AGENCY
40 CFR Parts 52 and 81
[MO 182-1182; FRL-7494-5]

Determination of Attainment of Ozone Standard, St. Louis Area;
Approval and Promulgation of Implementation Plans, and Redesignation of
Areas for Air Quality Planning Purposes, State of Missouri

AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.

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SUMMARY: EPA is determining that the St. Louis ozone nonattainment area
(St. Louis area) has attained the 1-hour ozone National Ambient Air
Quality Standard (NAAQS). The St. Louis ozone nonattainment area
includes the counties of Franklin, Jefferson, St. Charles, and St.
Louis as well as St. Louis City in Missouri and the counties of
Madison, Monroe, and St. Clair in Illinois. This determination is based
on three years of complete, quality-assured ambient air quality
monitoring data for the 2000 through 2002 ozone seasons that
demonstrate that the 1-hour ozone NAAQS has been attained in the area.
EPA is also determining that certain ozone attainment demonstration
requirements, along with certain other related requirements of part D
of title I of the Clean Air Act (CAA), are not applicable to the St.
Louis area.
EPA is also approving a request from the state of Missouri,
submitted on December 6, 2002, to redesignate the St. Louis area to
attainment of the 1-hour ozone NAAQS. In approving this request EPA is
also approving the state's plan for maintaining the 1-hour ozone NAAQS
through 2014, as a revision to the Missouri State Implementation Plan
(SIP). EPA is also finding adequate and approving the state's 2014
Motor Vehicle Emission Budgets (MVEBs) for volatile organic compounds
(VOCs) and nitrogen oxide compounds (NO_X) in the submitted
maintenance plan for transportation conformity purposes. Refer also to
a separate rule published today regarding similar approvals for the
state of Illinois.

DATES: This rule is effective May 12, 2003.

ADDRESSES: Relevant documents for this rule are available for
inspection at the Environmental Protection Agency, Region 7, Air
Planning and Development Branch, 901 North 5th Street, Kansas City,
Kansas 66101. Interested persons wanting to examine these documents
should make an appointment with the appropriate office at least 24
hours in advance.

FOR FURTHER INFORMATION CONTACT: Tony Petruska, (913) 551-7637,
(petruska.anthony@epa.gov).

SUPPLEMENTARY INFORMATION: Throughout this document whenever ``we,''
``us,'' or ``our'' is used, we mean EPA.

Table of Contents

I. What is the background for this action?
II. What actions are we taking and when are they effective?
III. Why are we taking these actions to redesignate the area?
IV. What are the effects of redesignation to attainment of the 1-
hour NAAQS?

[[Page 25419]]

V. What comments did we receive and what are our responses?
VI. Statutory and Executive Order Reviews.

I. What Is the Background for This Action?

On January 30, 2003, EPA published a final rule and two proposed
rules related to the St. Louis ozone nonattainment area (68 FR 4836, 68
FR 4842 and 68 FR 4847). The final rule found at 68 FR 4836 reinstated
and made effective a prior EPA finding that the St. Louis ozone
nonattainment area did not attain the 1-hour ozone standard by November
15, 1996 (based on 1994-1996 ozone data) and reinstated a
reclassification of the area to a serious nonattainment area. In
addition, in the January 30, 2003, final rule, EPA established a
schedule for submission of state implementation plan revisions and
established November 15, 2004, as the date by which the St. Louis area
must attain the ozone standard. A correction to this final rule was
published on February 13, 2003, which corrected a table entry (68 FR
7410). In the proposed rule found at 68 FR 4847, EPA proposed to
determine that the St. Louis ozone nonattainment area has attained the
1-hour ozone standard based on complete, quality-assured monitoring
data for 2000 through 2002. In addition, the proposed rule proposed to
approve requests from the states of Missouri and Illinois to
redesignate the St. Louis area to attainment with the 1-hour ozone
NAAQS, proposed to determine that certain requirements of the CAA are
not applicable, proposed to approve the states' maintenance plans as
revisions to the SIP, and proposed to find adequate and approve the
2014 motor vehicle emission budgets for volatile organic compounds and
nitrogen oxide compounds for transportation conformity purposes. In the
proposed rule found at 68 FR 4842, EPA proposed to approve a revision
to the state implementation plan for the inspection and maintenance (I/
M) program operating in the Missouri portion of the St. Louis area.
This rule is EPA's final action finding that the St. Louis ozone
nonattainment area has attained the 1-hour ozone standard, as well as
EPA's final action on the January 30, 2003, proposal found at 68 FR
4847 as it relates to the Missouri portion of the St. Louis
nonattainment area. As noted in the January 30, 2003, proposed rule on
page 4848, EPA received separate requests from Missouri and Illinois to
redesignate the St. Louis area to attainment. In the January 30, 2003,
proposed rule, EPA proposed actions related to both the Missouri and
Illinois portions of the nonattainment area. However, EPA stated that
it was considering issuance of two separate rules when it took final
action on the redesignation requests. We received no comments on this
aspect of the proposal. With the exception of the determination of
attainment, EPA is taking final action related to the Missouri portion
of the nonattainment area and is taking final action on the Illinois
portion of the St. Louis nonattainment area in separate rulemaking
actions. Section 107(d)(3)(v) provides, as a prerequisite to
redesignation, that: ``the State containing such area has met all
requirements applicable to the area under section 110 and part D.''
This section plainly shows that Congress meant for EPA to evaluate
whether each state requesting redesignation of an area has met the
applicable requirements. In addition, each state has authority only to
adopt and submit for approval a maintenance plan and a revision of its
SIP that are applicable to its territory. Since each state has the
authority only to request redesignation for the portion of the area
within its boundaries, and EPA evaluated each states' request for
redesignation separately, the final rules redesignating each states'
portion of the nonattainment area are being published separately.
However, EPA has concluded that in determining whether or not a
multistate area has attained the standard based upon complete, quality-
assured ambient air quality monitoring data, EPA will consider the
attainment status of the area as a whole. Therefore, EPA's finding that
the area has attained the NAAQS applies to the entire nonattainment
area, and we are publishing that finding in this rule. In another rule
published today, EPA references this finding and takes separate action
on a similar redesignation request and SIP submission by Illinois. See
67 FR 49600, July 31, 2002 (Reinstatement of Redesignation of Kentucky
Portion of Cincinnati-Hamilton area) for additional discussion of these
issues.
The history for this action has been set forth in detail in the
proposed rulemaking published January 30, 2003 (68 FR 4847, 4848-4849),
and is summarized below.
The Missouri portion of the St. Louis nonattainment area includes
Franklin, Jefferson, St. Charles, and St. Louis Counties and St. Louis
City. The Illinois portion of the St. Louis nonattainment area includes
Madison, Monroe, and St. Clair Counties (collectively referred to as
the Metro-East area).
The St. Louis area was designated as an ozone nonattainment area in
March 1978 (43 FR 8962). On November 15, 1990, the CAA Amendments of
1990 were enacted. Under section 107(d)(4)(A) of the CAA, on November
6, 1991 (56 FR 56694), the St. Louis area was designated as a moderate
ozone nonattainment area as a result of monitored violations of the 1-
hour ozone NAAQS during the 1987-1989 period. On January 30, 2003, EPA
reclassified the area to a serious nonattainment area, effective
January 30, 2003.
The states adopted and implemented emission control programs
required under the CAA to reduce emissions of VOC and NO_X.
These emission control programs include stationary source reasonably
available control technology (RACT), vehicle I/M programs,
transportation control measures (TCMs), and other measures (see the
analysis and discussion of specific emission control measures at 68 FR
4847). As a result of the emission control programs, ozone monitors in
the St. Louis area have recorded three years of ozone monitoring data
for the 2000-2002 period showing that the area has attained the 1-hour
ozone NAAQS.
On December 6, 2002, the Missouri Department of Natural Resources
(MDNR) submitted a Redesignation Demonstration and Maintenance Plan for
the Missouri Portion of the St. Louis ozone nonattainment area along
with a request to redesignate the Missouri portion of the St. Louis
nonattainment area to attainment of the 1-hour ozone NAAQS. Included in
the Redesignation Demonstration and Maintenance Plan for the Missouri
Portion of the St. Louis nonattainment area is a plan to maintain the
1-hour ozone NAAQS for at least the next 10 years, and the 2014 MVEBs
for transportation conformity purposes.

II. What Actions Are We Taking and When Are They Effective?

After consideration of the comments received in response to the
January 30, 2003, proposal, as described in section V below, we are
taking the following actions:

A. Determination of Attainment

EPA is determining that the St. Louis ozone nonattainment area,
consisting of both the Missouri and the Illinois portions of the area,
has attained the 1-hour ozone standard.
EPA is also determining that certain attainment demonstration
requirements (section 172(c)(1) of the CAA), along with certain other
related requirements, of part D of title I of the CAA, specifically the
section 172(c)(9) contingency measure requirement (measures needed to
mitigate a state's

[[Page 25420]]

failure to achieve reasonable further progress toward, and attainment
of, a NAAQS), the section 182 attainment demonstration and rate of
progress (ROP) requirements, and the section 182(j) multi-state
attainment demonstration requirement, are not applicable to the St.
Louis area.
On January 30, 2003 (68 FR 4847), EPA proposed that the St. Louis
area had attained the standard based on 2000-2002 monitoring data. With
this finding, EPA also proposed that certain requirements, including an
attainment demonstration, were no longer applicable as the area had
attained the standard. EPA has explained at length in other actions its
rationale for the reasonableness of this interpretation of the CAA and
incorporates those explanations by reference. See (67 FR 49600)
(Cincinnati-Hamilton, Kentucky, July 31, 2002); (66 FR 53095)
(Pittsburgh-Beaver Valley, Pennsylvania, October 19, 2001); (65 FR
37879) (Cincinnati-Hamilton, Ohio and Kentucky, June 19, 2000); (61 FR
20458) (Cleveland-Akron-Lorain, Ohio May 7, 1996); (60 FR 36723) (July
18, 1995) Salt Lake and Davis Counties, Utah); (60 FR 37366) (July 20,
1995), (61 FR 31832-31833) (June 21, 1996) (Grand Rapids, MI). The
United States Court of Appeals for the Tenth Circuit has upheld EPA's
interpretation. Sierra Club v. EPA, 99 F. 3d 1551 (10th Cir. 1996).
EPA reiterates the position set forth in its prior rulemaking
actions and in the January 30, 2003 (68 FR 4847) proposed rulemaking
for the St. Louis area. Subpart 2 of part D of title I of the CAA
contains various air quality planning and SIP submission requirements
for ozone nonattainment areas. EPA believes it is reasonable to
interpret the provisions regarding Reasonable Further Progress (RFP)
and attainment demonstrations, along with other certain other related
provisions, not to require SIP submissions if an ozone nonattainment
area subject to those requirements is monitoring attainment of the
ozone standard (i.e., attainment of the NAAQS demonstrated with three
consecutive years of complete, quality-assured, air quality monitoring
data). EPA interprets the general provisions of subpart 1 of part D of
title I (sections 171 and 172) not to require the submission of SIP
revisions concerning RFP, attainment demonstrations or section
172(c)(9) contingency measures. As explained in a memorandum from John
S. Seitz, Director, Office of Air Quality Planning and Standards,
entitled ``Reasonable Further Progress, Attainment Demonstration, and
Related Requirements for Ozone Nonattainment Area Meeting the Ozone
National Ambient Air Quality Standard,'' dated May 10, 1995, EPA
believes it is appropriate to interpret the more specific attainment
demonstration and related provisions of subpart 2 in the same manner.
See Sierra Club v. EPA, 99 F. 3d. 1551 (10th Cir. 1996).
The attainment demonstration requirements of section 182(b)(1)
require that the plan provide for ``such specific annual reductions in
emissions * * * as necessary to attain the national primary ambient air
quality standard by the attainment date applicable under the CAA.'' If
an area has, in fact, monitored attainment of the relevant NAAQS, EPA
believes there is no need for an area to make a further submission
containing additional measures to achieve attainment. This is also
consistent with the interpretation of certain section 172(c)
requirements provided by EPA in the General Preamble to Title I. As EPA
stated in the General Preamble, no other measures to provide for
attainment would be needed by areas seeking redesignation to attainment
since ``attainment will have been reached'' (57 FR 13564). Upon
attainment of the NAAQS, the focus of state planning efforts shifts to
the maintenance of the NAAQS and the development of a maintenance plan
under section 175A.
Similar reasoning applies to other related provisions of subpart 2.
The first of these are the contingency measure requirements of section
172(c)(9) of the CAA. EPA has previously interpreted the contingency
measure requirements of section 172(c)(9) as no longer being applicable
once an area has attained the standard since those ``contingency
measures are directed at ensuring RFP and attainment by the applicable
date'' (57 FR 13564).
The state must continue to operate an appropriate network, in
accordance with 40 CFR part 58, to verify the attainment status of the
area. The air quality data relied upon to determine that the area is
attaining the ozone standard must be consistent with 40 CFR part 58
requirements and other relevant EPA guidance and recorded in EPA's
Aerometric Information Retrieval System (AIRS).
EPA has reviewed the ambient air monitoring data for ozone
(consistent with the requirements contained in 40 CFR part 58 and
recorded in EPA's AIRS) for the St Louis ozone nonattainment area from
the 2000 to 2002 ozone seasons. EPA has also reviewed the preliminary
data collected to date for the 2003 ozone season (for St. Louis, the
ozone season is April 1 through October 31 of each year). On the basis
of this review, EPA has determined that the area has attained the 1-
hour ozone standard during the 2000-2002 period and continues to attain
the standard, and therefore is not required to submit an attainment
demonstration and a section 172(c)(9) contingency measure plan, nor
does it need any other measures to attain the 1-hour ozone standard.

B. Redesignation of Missouri Portion of the St. Louis Area to
Attainment

Although EPA is determining that the entire St. Louis nonattainment
area has attained the 1-hour ozone standard, EPA has determined that it
is appropriate to take final action related to Missouri's request to
redesignate the Missouri portion of the St. Louis nonattainment area
and take final action related to Illinois' request to redesignate the
Illinois portion of the St. Louis nonattainment area in separate
rulemaking actions being published today. In the January 30, 2003,
proposal, EPA stated that it was considering publishing separate
rulemakings for Missouri and Illinois (68 FR 4848). We received one
comment in support of publishing separate rulemakings and no adverse
comments. In this rulemaking, EPA is taking the following actions with
respect to the Missouri portion of the St. Louis nonattainment area:
EPA is approving a request from the state of Missouri to
redesignate the Missouri portion of the St. Louis nonattainment area to
attainment of the 1-hour ozone NAAQS.
In addition, EPA is taking the following actions:
1. Approving Missouri's plan for maintaining the 1-hour ozone NAAQS
through 2014, as a revision to the Missouri SIP;
2. Finding adequate and approving the 2014 MVEBs of 47.14 tons per
ozone season weekday for VOC and 68.59 tons per ozone season weekday
for NO_X in the submitted maintenance plans for
transportation conformity purposes; and,
3. Determining that the attainment demonstration (and related
contingency measure requirements) and reasonably available control
measure (RACM) requirements of the CAA are not applicable.

C. Effective Date of These Actions

EPA finds that there is good cause for this determination of
attainment, redesignation to attainment and SIP revision to become
effective immediately upon publication because a delayed effective date
is unnecessary due to the nature of a redesignation to attainment which
relieves the area from certain CAA requirements that would otherwise
apply to it. The immediate

[[Page 25421]]

effective date for this action is authorized under both 5 U.S.C.
553(d)(1), which provides that rulemaking actions may become effective
less than 30 days after publication if the rule ``grants or recognizes
an exemption or relieves a restriction'' and section 553(d)(3) which
allows an effective date less than 30 days after publication ``as
otherwise provided by the agency for good cause found and published
with the rule.''
In addition, as indicated above, the January 30, 2003, final rule
reclassified the St. Louis area to a ``serious'' nonattainment area and
established a schedule for submission of SIP revisions fulfilling the
requirements for serious ozone nonattainment areas. Upon the effective
date of this rule, the state of Missouri will be relieved of the
obligation to develop and submit these SIP revisions. In addition, the
Missouri rules adopted to meet the requirements of title V of the CAA,
provide that in a ``serious'' area, stationary sources with potential
emissions of VOCs and NO_X greater than 50 tons per year are
major sources. As such, these major sources are subject to the title V
permit program and are required to submit title V permit applications
within twelve months of January 30, 2003. Upon the effective date of
this rule, stationary sources which are newly subject to the title V
permitting program as a result of the January 30, 2003,
reclassification to a serious nonattainment area will be relieved of
the requirement to submit title V permit applications. In a separate
rulemaking, EPA is redesignating the Illinois portions of the St. Louis
area to attainment. Additional requirements specific to the Illinois
portion of the St. Louis area are described in that separate rulemaking
and are also being lifted as a result of that portion's redesignation
to attainment. EPA finds that good cause exists for this final rule
being immediately effective since it relieves the state of Missouri as
well as stationary sources of certain restrictions which would
otherwise apply.

III. Why Are We Taking These Actions To Redesignate the Area?

EPA has determined that the St. Louis area has attained the 1-hour
ozone standard. In addition, EPA has determined that the state of
Missouri has demonstrated that the criteria for redesignation of the
Missouri portion of the area from nonattainment to attainment have been
met.
In the January 30, 2003, proposed rule at 68 FR 4847, EPA described
the applicable criteria for redesignation to attainment. Specifically,
section 107(d)(3)(E) allows for redesignation providing that: (1) The
Administrator determines that the area has attained the applicable
NAAQS; (2) the Administrator has fully approved the applicable
implementation plan for the area under section 110(k); (3) the
Administrator determines that the improvement in air quality is due to
permanent and enforceable reductions in emissions resulting from
implementation of the applicable implementation plan and applicable
Federal air pollutant control regulations and other permanent and
enforceable reductions; (4) the Administrator has fully approved a
maintenance plan for the area as meeting the requirements of section
175A; and, (5) the state containing such area has met all requirements
applicable to the area under section 110 and part D.
EPA has determined that the St. Louis area has attained the
applicable NAAQS. EPA has fully approved the applicable implementation
plan for the Missouri portion of the St. Louis area under section
110(k). EPA has determined that the improvement in air quality is due
to permanent and enforceable reductions in emissions resulting from
implementation of the applicable implementation plan and applicable
Federal air pollutant control regulations and other permanent and
enforceable reductions. EPA has fully approved a maintenance plan for
the Missouri portion of the area as meeting the requirements of section
175A. Missouri has met all requirements applicable to the Missouri
portion of the area under section 110 and part D.
By finding that the maintenance plan provides for maintenance of
the NAAQS through 2014, EPA is hereby finding adequate and approving
the 2014 MVEBs contained within the maintenance plan. The MVEB for
NO_X in the Missouri portion of the St. Louis area is 68.59
tons per ozone season weekday. The MVEB for VOCs in the Missouri
portion of the St. Louis area is 47.14 tons per ozone season weekday.
The rationale for these findings is as stated in this rulemaking
and the January 30, 2003, proposed rule found at 68 FR 4847.

IV. What Are the Effects of Redesignation to Attainment of the 1-Hour
NAAQS?

These actions determine that the area attained the 1-hour ozone
standard and that certain other related requirements of part D of title
I of the CAA, specifically the section 172(c)(9) contingency measure
requirement (measures needed to mitigate a state's failure to achieve
reasonable further progress toward, and attainment of, a NAAQS), the
section 182 attainment demonstration and rate of progress requirements,
and the section 182(j) multi-state attainment demonstration requirement
are not applicable to the St. Louis area. EPA's determination that the
St. Louis area has met the 1-hour ozone standard relieves the states
from the obligation to meet certain additional requirements, which
apply to areas not attaining that standard.
EPA notes that the area is likely to be designated nonattainment
for the 8-hour ozone standard and would be subject to any additional
requirements as a result of such designation. EPA also notes that it is
not revoking the 1-hour standard for the St. Louis area.
Approval of the Missouri redesignation request changes the official
designation for the 1-hour ozone NAAQS found at 40 CFR part 81 for the
Missouri portion of the St. Louis area, including the City of St Louis,
and the Counties of Franklin, Jefferson, St. Charles, and St. Louis
from nonattainment to attainment. It also incorporates into the
Missouri SIP a plan for maintaining the 1-hour ozone NAAQS through
2014. The plan includes contingency measures to remedy any future
violations of the 1-hour ozone NAAQS, and includes VOC and
NO_X MVEBs for 2014 for the Missouri portion of the St. Louis
area.

V. What Comments Did We Receive and What Are Our Responses?

We received five letters regarding the January 30, 2003, proposed
rule found at 68 FR 4847. Four of the letters generally supported the
rulemaking action. Two of the four letters in support of the rulemaking
action raised issues to which EPA is responding in this section. One of
the five letters contained adverse comments. A summary of the comments
and EPA's responses to them are provided below. This discussion
addresses comments relating to the St. Louis area as a whole, and
comments specifically relating to the Missouri portion of the area.
Comments relating specifically to the Illinois portion of the area are
addressed in the final rule for Illinois published elsewhere in this
Federal Register.

A. Comment Related to Meeting the Criteria for Redesignation to Attainment

Comment 1: The St. Louis area has failed to meet any of the five
criteria specified in section 107(d)(3)(E) of the CAA for redesignation
to attainment.
Response 1: EPA's determination that the St. Louis area has
attained the ozone standard is set forth in section II.A above. EPA has
further found that the area has met all of the five criteria

[[Page 25422]]

specified in section 107(d)(3)(E) of the CAA for redesignation to
attainment. Below are specific comments and responses raised by the
commenter regarding each criterion.

B. Comments Related to Criterion 1: The Area Must Be Attaining the 1-
Hour Ozone NAAQS

Comment 2: Monitoring data are not representative of air quality
conditions. Monitoring data collected on Labor Day weekend in 2002 are
``hopelessly contaminated'' due to voluntary emission reductions
undertaken by industry and others.
Response 2: Section 107(d)(3)(E)(i) of the CAA states that one
criterion for redesignation to attainment is that EPA must determine
that the NAAQS has been attained. The regulations at 40 CFR part 58
specify data collection and quality assurance procedures. For ozone, an
area is attaining the 1-hour ozone NAAQS if there are no violations, as
determined in accordance with 40 CFR 50.9 and appendix H. The
regulation at 40 CFR 50.9 states ``the standard is attained when the
expected number of days per calendar year with maximum hourly average
concentrations above 0.12 part per million is equal to or less than 1
as determined by appendix H.'' Appendix H states, ``The basic principle
in making this determination is relatively straightforward. . . . In
its simplest form, the number of exceedances at a monitoring site would
be recorded for each calendar year and then averaged over the past 3
calendar years to determine if this average is less than or equal to
1.'' The monitoring data for the St. Louis nonattainment area
demonstrate that the estimated number of exceedances per year averaged
over three years (2000 through 2002) is 1.0 or less at all monitoring
sites in the area. In the case of St. Louis, all of the data collected
are reviewed, quality assured and submitted to EPA's Air Quality System
(AQS) database. EPA conducts a number of activities to determine that
the data meet the data collection and quality assurance procedures of
40 CFR part 58 including the following:

--EPA ensures that the state (and local agencies) is performing quality
assurance/quality control (QA/QC) checks properly through systems
audits as required per 40 CFR part 58, appendix A. During these systems
audits EPA ensures that states are properly calibrating instruments,
properly performing precision and span checks on instruments, and
properly conducting audits of the instruments as required in 40 CFR
part 58, appendix A.
--EPA chooses several hourly ozone values and tracks those data points
from their collection at the monitor through their data handling
procedures, including QA/QC procedures, to its final destination in the
AQS database.
--To ensure quality data, as required by 40 CFR part 58, appendix A,
prior to the start of ozone season each year, EPA certifies at least
one primary standard ozone photometer for each of the state and local
agencies. These primary ozone photometers stay in the state/local
laboratories. Transfer standard photometers are verified against the
primary photometer and are used to calibrate the ozone analyzers in the
field. Thus, all of the data collected is traceable back to EPA's
primary photometer.
--EPA, as well as the quality assurance groups of the state and local
agencies, conduct audits on the ozone instruments collecting the data.
These audits are required to be performed quarterly as per 40 CFR part
58, appendix A. EPA audits each ozone instrument at least once per
ozone season. This ensures that the instrument is operating properly
and collecting accurate data, and it also acts as a check on the state
and local quality assurance groups to make sure that the audits they
have conducted are accurate.
--As required by 40 CFR part 58, appendix A, Precision and Span checks
are performed every two weeks by the agency operating the instrument.

EPA believes that any voluntary measures which may have been taken
by industry and others over a two- or three-day period in this three-
year time period do not render the air quality monitoring data
unrepresentative of the air quality. The data would only be
``contaminated'' if there had been an error with respect to collection
and quality assurance of the data, which there was not. The commenter
offers no information indicating data collection was improper. In
addition, even if these activities by the community were relevant to
whether the area had attained, there is no evidence that emissions were
actually reduced to an extent which would have a significant effect on
ozone levels. See response to comment 18 below regarding further
discussion on the ``voluntary reductions'' during the Labor Day weekend
in 2002. In fact, as explained in the January 30, 2003, proposal at 68
FR 4856-4858, and in section V.D. below, the monitored improvements in
air quality were due to permanent and enforceable emission reductions.
For example, as explained further in response to comment 19, the
Missouri centralized motor vehicle inspection and maintenance program
began in April 2000, the first year of the 2000-2002 time period. The
use of reformulated gasoline began in 1999 and achieved additional
reductions during the 2000-2002 time period. The monitoring data
accurately reflected actual air quality conditions. See response to
comment 19 below regarding EPA's conclusion that improvements in air
quality are attributable to permanent and enforceable reductions in
ozone precursor emissions.
Comment 3: EPA's proposal ignores the second component discussed in
a September 4, 1992, redesignation guidance document from John Calcagni
entitled ``Procedures for Processing Requests to Redesignate Areas to
Attainment'' (Calcagni memo) to EPA regional offices, that the
determination of attainment should rely not only on monitored values,
but on supplemental EPA-approved modeling. For St. Louis, monitored
data runs directly counter to air quality modeling. The modeling
supported the contention that the NAAQS could be attained only in 2004
after all control measures are adopted. Thus, the monitored attainment
is a ``fluke'' explainable by factors other than the success of the
pollution control measures. In addition, based on the Calcagni memo the
commenter believes that supplemental ozone modeling may be necessary to
determine the representativeness of the monitored data. Without such
supplemental modeling, the commenter asserts that the January 30, 2003,
proposed rule's implicit conclusion that the St. Louis area ozone data
are ``representative'' is baseless.
Response 3: The commenter cites a policy memorandum entitled
``Procedures for Processing Requests to Redesignate Areas to
Attainment'' dated September 4, 1992 (Calcagni memo), which states that
there are two components in determining that an area has met the
section 107(d)(3)(E)(i) requirement. This policy states the following:

The state must show that the area is attaining the applicable
NAAQS. There are two components involved in making this
demonstration which should be considered interdependently. The first
component relies upon ambient air quality data. * * * The second
component relies upon supplemental EPA-approved air quality
modeling. No such supplemental modeling is required for
O₃

[[Page 25423]]

(ozone) nonattainment areas seeking redesignation * * * (pages 2 and 3).

This document explains that supplemental modeling may be needed,
for example, in sulfur dioxide and carbon monoxide areas, where
emissions are localized and a small number of monitors may not be
representative of air quality (page 3). In contrast, ozone is not a
localized pollutant, and the St. Louis area has an extensive monitoring
network consisting of nineteen monitors operating each year from 2000
through 2002 as described in EPA's proposal at 68 FR 4850. Therefore,
consistent with the language in the policy and the rationale in calling
for modeling in some cases for some pollutants and not in other cases,
modeling is not required as part of this redesignation. Neither section
107(d)(3)(E) nor the policy referenced by the commenter requires
modeling as a prerequisite to redesignation of an ozone nonattainment
area. In addition, no modeling was conducted as part of the
redesignation requests submitted by Missouri or Illinois. Therefore,
EPA does not believe that the monitored data runs counter to air
quality modeling. See Wall v. EPA, 265 F.3d 426 (6th Cir. 2001), and
the redesignations for Pittsburgh (66 FR 53094, October 19, 2001), and
Cincinnati (65 FR 37879, June 19, 2000). See response to comments 10,
19, 21, 23, 24, 26, 37 below regarding further discussion of modeling
issues.
Commenter's contention that attainment cannot be reached until at
least 2004 is addressed below in response to comments 21 and 24.
In addition, the correlation between air quality improvements and
permanent and enforceable emission reductions, demonstrating that
monitored attainment is not a ``fluke'' is described in detail in the
proposal and section V.D below.
The ozone modeling approaches used do not support any direct
comparisons between ozone modeling results and monitored ozone
concentrations for years other than a monitored and modeled base
period. Although statistical comparisons are made between monitored
ozone data and modeled base period ozone concentrations to validate
ozone modeling results, ozone models are not designed to explicitly
model ozone concentrations at specific locations or to exactly predict
future ozone concentrations that can be compared to monitored ozone
concentrations on a site-by-site basis. Ozone models are designed to
primarily predict the relative impacts of emission changes on future
peak ozone levels assuming the same meteorological conditions that are
modeled for the base period. Such modeling techniques produce results
with considerable uncertainty (relative to time- and location-specific
monitored ozone concentrations) when one actually compares future
modeled results with monitored ozone concentrations for the same years.
The commenter errs in trying to force comparisons not supported by the
existing science.
What the modeling results do imply is that, as regional
NO_X emission controls are implemented through statewide
rules in Illinois, Missouri, and other states, peak ozone levels in the
St. Louis area are expected to decrease. This increases the likelihood
of maintaining the ozone standard in the St. Louis area, thus
supporting the approval of the state's ozone redesignation request.
Illinois and Missouri are committed to implement statewide
NO_X emission controls regardless of the attainment status of
the St. Louis area. Both states are currently implementing statewide
NO_X control rules.
Comment 4: The monitored data do not support a conclusion of
continued attainment since the trend is toward increases in exceedances
because the number of exceedances tripled from 2000 to 2001 and more
than doubled from 2001 to 2002 showing an upward trend in peak ozone
concentrations. The commenter notes that, if the same number of
exceedances that occurred in 2002 occur in 2003 or 2004, the area will
again violate the one-hour ozone standard.
Response 4: See response to comment 20 below for our detailed
response to the comment relating to air quality trends. The
determination of attainment, as explained in the January 30, 2003,
proposal, in section II.A. above, and in response to comment 2, is
based on the requirements of section 107(d)(3)(E)(i) and EPA's
regulation which defines attainment of the ozone standard. The
regulatory definition is based on design values over a 3-year period,
not on year-to-year trends within the three-year period. It would be
inconsistent with the regulation to adopt an additional criterion for
determining attainment.
It should be noted that a ``worsening'' ozone trend for the St.
Louis area can only be discerned for the 2000-2002 period by combining
the annual number of exceedances for all monitoring sites in the area
(by totaling the number of exceedances for each year for all monitoring
sites combined). This approach is technically flawed. The ozone
standard is based on assessing the peak ozone data for each monitoring
site individually not by cumulating the data for all sites. Review of
the yearly exceedance data for each monitoring site, as given in Table
1 in the January 30, 2003, proposed rule (68 FR 4850) and in response
to comment 20 below, shows that no consistent ozone exceedance rate
trend can be established for the individual monitoring sites for this
period. For example, the West Alton site experienced one ozone
exceedance per year with no up or down trend. The Wood River monitor in
Illinois increased from zero exceedances in 2000 to one exceedance in
2001 and back down to zero exceedances in 2002. Many monitors continued
to record zero exceedances throughout the 2000-2002 period as noted
above. Some monitors, which recorded zero exceedances in 2000 and 2001,
recorded one or two exceedances in 2002, hardly a consistent, robust
trend. Contrary to the commenter's assertion, on a monitor-by-monitor
basis, which is the basis for assessing compliance with the 1-hour
ozone standard, there is no consistent ``worsening'' trend in peak
ozone concentrations.
Comment 5: EPA asserts that the data is ``quality assured'' but
provided no explanation. EPA must demonstrate that the data is quality
assured. EPA must document the adequacy of the states' quality
assurance plan. Also, the commenter questions whether the data relied
on for the attainment determination was quality-assured since it was
entered in AIRS earlier than usual.
Response 5: As indicated in the response to comment 2 above, the
regulations at 40 CFR part 58 specify data collection and quality
assurance procedures. The Calcagni memo on page 2 specifies that the
data should be collected and quality-assured in accordance with 40 CFR
part 58 and recorded in AIRS in order for it to be available to the
public for review. The monitoring data for the St. Louis area was
quality assured and entered into AIRS in accordance with these
requirements.
Appendix A to 40 CFR part 58 specifies the quality assurance
requirements for state and local air monitoring stations. The
regulation at 40 CFR 58.35(c) requires that the monitoring data be
entered into AIRS within 90 days after the end of the calendar quarter
in which it is collected. Thus, monitoring data collected through
September 2002 must be quality assured and entered into AIRS by
December 31, 2002. Monitoring data for October 2002 must be quality
assured and entered into AIRS by March 31, 2003.

[[Page 25424]]

Monitoring data collected in a calendar quarter can be quality assured
and entered into AIRS at any time prior to 90 days after the end of
that quarter.
The monitoring data is quality assured and entered into AIRS by the
state and local agencies in the St. Louis area. The regulation at 40
CFR 58.20 requires states to adopt and submit to EPA revisions to the
SIP which provide for meeting the requirements of appendix A. On
September 27, 1984 (49 FR 38103), EPA approved Missouri's Air Quality
Monitoring Plan. EPA stated in this September 27, 1984, rulemaking that
``the Missouri Air Quality Monitoring Plan satisfies the requirements
of 40 CFR 58.20.'' On March 4, 1981 (46 FR 15136), EPA approved
Illinois' Air Quality Surveillance Plan. EPA stated in this March 4,
1981, rulemaking that EPA has reviewed the plan and ``it meets the
requirements of * * * EPA regulations in 40 CFR part 58.'' As part of
the September 27, 1984, and March 4, 1981, rulemakings the public was
provided the opportunity to review and comment on Missouri's and
Illinois' quality assurance procedures. Pursuant to the Calcagni memo,
page 3, and upheld in Wall v. EPA (265 F.3d. 426, 437), an EPA action
on a redesignation request does not mean that earlier issues with
regard to the SIP will be reopened. Thus, there is no requirement to
present quality assurance procedures in this rulemaking.
In addition to Missouri's Air Quality Monitoring Plan and Illinois'
Air Quality Surveillance Plan, EPA reviewed and approved the States'
Quality Management Plans (QMP). Under the states' QMP, the state and
local agencies conducting the ambient monitoring develop Quality
Assurance Project Plans (QAPP). It is through the QMP and QAPP that EPA
reviewed and approved the states' and local agencies' quality assurance
procedures. In order to verify that the state and local agencies
followed these procedures and that the data meets the data collection
and quality assurance procedures of 40 CFR part 58, EPA conducted the
actions listed in the response to comment 2 above.

C. Comments Related to Criterion 2: The Area Must Have a Fully Approved
SIP Under Section 110(k)

Comment 6: The serious area SIP requirements of the CAA are
applicable to the St. Louis area. These requirements have not been
promulgated by the states and there is no ``claim'' that they could not
have been submitted with the redesignation request. Thus, the SIPs are
not ``fully approved.'' In addition, the Calcagni memo includes
procedures suggested by EPA for reducing the stringency of the control
measures to become part of the contingency measure. The states have not
done these procedures.
Response 6: The SIP which is required to be ``fully approved''
under criterion 2 is the ``applicable'' implementation plan (section
107(d)(3)(E)(ii)). This section requires that the SIP must be ``fully
approved'' under section 110(k) rather than partial, conditional, or
limited approval (Calcagni memo, page 3). Section 107(d)(3)(E)(v)
requires the SIP to include ``all requirements applicable to the area
under Section 110 and Part D.'' This comment relates to the issue of
which requirements are ``applicable,'' rather than whether the SIP is
fully approved. The commenter asserts, without explanation, that the
statute requires EPA to determine that the ``serious'' area
requirements are applicable to its consideration of the redesignation
request for the area. However, the CAA is not as prescriptive as the
commenter assumes. (See, Wall v. EPA, 265 F.3d 426,438 (6th Cir. 2001)
which states: ``The statute, however, does not describe how the EPA is
to decide which Part D requirements are ``applicable'' in evaluating a
redesignation request.'')
EPA has established a policy to provide guidance in determining how
to apply the statutory criterion with respect to which requirements are
applicable in reviewing a redesignation request. As stated in the
January 30, 2003, proposed rule (page 4851), the September 4, 1992,
Calcagni memo (see ``Procedures for Processing Requests to Redesignate
Areas to Attainment,'' Memorandum from John Calcagni, Director, Air
Quality Management Division, September 4, 1992) describes EPA's
interpretation of the section 107(d)(3)(E) requirement. Under this
interpretation, states requesting redesignation to attainment must meet
the relevant CAA requirements that come due prior to the submittal of a
complete redesignation request. Areas may be redesignated even though
they have not adopted measures that come due after the submission of a
complete redesignation request. A detailed discussion of EPA's
rationale for this interpretation is contained in the rule
redesignating Detroit-Ann Arbor, 60 FR 12459, 12465-12466 (March 7,
1995). Pursuant to the January 30, 2003, final rule reclassifying the
St. Louis area to ``serious'' (68 FR 4836), the serious nonattainment
area requirements are due on January 30, 2004. The final rule has not
been timely challenged under section 307(b)(1) of the CAA. Thus, the
serious nonattainment area requirements due date is January 30, 2004.
Since the serious area requirements are not yet due, the SIP is not
deficient because the serious area requirements have not been included.
EPA policy and a reasonable application of sections 107(d)(3)(E)(ii)
and (v) allow for an area to be redesignated even though the area has
not adopted measures which are not yet due. EPA has consistently
applied this policy and interpretation in other redesignations
including the Detroit-Ann Arbor redesignation cited above.
In addition, there is no requirement in section 107(d)(3)(E) that
states must ``claim'' (or demonstrate) that they could not have
submitted the serious area SIP revisions or any additional revisions at
the time of the redesignation requests, if those requirements are not
applicable to the area when the request is made. EPA's action to
reclassify the area to a serious nonattainment area was published in
the Federal Register after both states had submitted their
redesignation requests to attainment, and it established a deadline for
submission of the serious area requirements which had not yet passed,
and still remains in the future. Thus, Missouri was not required to
include in its request a ``claim'' that the state cannot complete the
serious area requirements.
Finally, the Calcagni memo discusses the statutory requirement that
the state must implement all measures included in the SIP prior to
redesignation (pages 12-13). (In response to comment 32, EPA discusses
how this requirement has been met.) This requirement does not expand
the universe of requirements which are ``applicable'' for purposes of
redesignation. Unless the serious area requirements are applicable to
an area, and already contained in a SIP prior to redesignation, the
discussion in the Calcagni memo does not relate to the issue raised by
the commenter.
Because the serious area requirements are not applicable
requirements for St. Louis, for the reasons discussed above, and are
not included in the SIP for St. Louis, the guidance in the Calcagni
memo and in a memorandum entitled ``State Implementation Plan (SIP)
Requirements for Areas Submitting Requests for Redesignation to
Attainment of the Ozone and Carbon Monoxide (CO) National Ambient Air
Quality Standards (NAAQS) on or after November 15, 1992'' dated
September 17, 1993 (Shapiro memo), relating to mechanisms for
converting part D measures into contingency measures is

[[Page 25425]]

not relevant for purposes of this redesignation.
Comment 7: The proposed rulemaking suggests that a SIP meeting the
serious area requirements need not be fully approved because such a
plan is not yet due. The CAA does not make an exception for SIP
revisions that have or have not become due. In fact, the serious area
requirements have, as a matter of law, become due. The plans were due
by June 14, 1998, and no later than May 18, 2002, pursuant to previous
EPA and Court actions. The commenter stated that the May 18, 2002, date
was set by EPA in a March 19, 2001, rulemaking, and that the effect of
a decision by the Court of Appeals for the Seventh Circuit was to
reinstate this submission date.
Response 7: Section 107(d)(3)(E)(ii) requires that the applicable
SIP for the area must be fully approved under section 110(k). As
discussed in the response to comments 6 and 8, the applicable SIPs for
the St. Louis area are fully approved, and the serious area
requirements have not yet become due. In making this determination, EPA
is not creating an ``exception'' to the statutory requirements for
approved SIPs, but is determining that SIP revisions which are not yet
due are not ``applicable'' for purposes of section 107(d)(3)(E)(ii) and
(v). As stated in the January 30, 2003, final rule at 68 FR 4838, on
November 25, 2002, the Seventh Circuit Court of Appeals vacated a June
26, 2001, rule extending the St. Louis area's attainment date, and
remanded to EPA for ``entry of a final rule that reclassifies St Louis
as a serious nonattainment area effective immediately * * *'' (Sierra
Club and Missouri Coalition for the Environment v. EPA, 311 F. 3d 853
(7th Cir. 2002)). In response to the Court's order, and in accordance
with section 181(b)(2) of the CAA, EPA reinstated the nonattainment
determination and reclassification contained in the March 19, 2001,
rulemaking (66 FR 15585). In the January 30 rule, EPA also established
a deadline of 12 months after January 30, 2003, for the states to
submit the serious area requirements. The rationale for the deadline is
stated in the January 30, 2003, final rule (68 FR 4838). The January
30, 2003, final rule was not challenged and this redesignation
rulemaking does not reopen the January 30 rulemaking. Comments on the
appropriate deadline for the serious area requirements are beyond the
scope of this rule.
With respect to the commenter's assertion that the serious area
requirements should have been due by June 14, 1998, this is based on an
argument made by the commenter in the U.S. District Court and the Court
of Appeals for the District of Columbia that the reclassification of
the St. Louis area to serious should have been made retrocative to
1997, with the serious area measures due in 1998. This argument is not
only outside the scope of this rulemaking as explained previously, but
it was rejected by both Courts (See, Sierra Club v. Whitman, 285 F.3d,
63, 68 (D.C. Cir. 2002)). The Courts rejected the notion that
retroactive SIP submission dates should be imposed because they would
have passed before the area had notice and opportunity to meet the
deadlines. See also, Metropolitan Washington, DC, Maryland and Virginia
Determination of Nonattainment (68 FR 3410, January 24, 2003). As
explained above, EPA's determination that the serious area requirements
are not ``applicable'' with respect to this redesignation because they
are not yet due is consistent with the CAA, with the January 30, 2003,
final rule, with applicable EPA policy, with relevant judicial
decisions, and with a long history of prior redesignation actions.
Comment 8: There is no ``fully approved'' or even a partially
approved SIP because the June 26, 2001, rule was vacated by the Court
of Appeals for the Seventh Circuit.
Response 8: This comment refers to both the Missouri and Illinois
portions of the St. Louis area. EPA is hereby providing a response
regarding the Missouri portion of the St. Louis area. See the
rulemaking in today's Federal Register regarding redesignation of the
Illinois portion of the St. Louis area for EPA's response to this
comment as it pertains to the Illinois portion of the St. Louis area.
In the January 30, 2003, proposed rule at 68 FR 4850 through 4856,
EPA described the actions taken by EPA in the June 26, 2001, rule which
were vacated by the Court of Appeals for the Seventh Circuit. Also, in
the January 30, 2003, proposed rule at 68 FR 4850 through 4856, EPA
reproposed to approve some requirements, and explained that certain
additional actions vacated by the Court were no longer applicable
requirements since the area has attained the NAAQS. As discussed in the
January 30, 2003, proposed rule, the additional actions vacated by the
Court which are no longer applicable include the contingency measure
requirements of section 172(c), additional RACM requirements of section
172(c)(1) and section 182(b), and the attainment demonstration
requirements of section 182(b)(1). That discussion is incorporated
herein. See also the discussion in section II.A concerning the
inapplicability of certain requirements. In the June 26, 2001, rule,
EPA took the following relevant actions: approved Missouri's and
Illinois' 1-hour ozone attainment demonstration; found that the St.
Louis ozone nonattainment area met the RACM requirements of the CAA;
found that the contingency measures identified by the states of
Illinois and Missouri are adequate; approved the Illinois and Missouri
MVEBs; approved an exemption from the oxides of nitrogen
(NO_X) emission control requirements for RACT and disapproved
an exemption from the NO_X new source review (NSR) and
NO_X conformity requirements for the Illinois portion of the
St. Louis ozone nonattainment area. EPA has determined, for the reasons
stated in this rule and in the proposed rule, that the attainment
demonstration, and RACM requirements, are no longer applicable
requirements since the area has attained the NAAQS. In this rulemaking,
EPA is approving contingency measures as part of Missouri's maintenance
plan, and approving MVEBs for 2014, for the Missouri portion of the
area. In a separate rulemaking in today's Federal Register, EPA is
approving revisions to Missouri's I/M rule.
To be considered fully approved pursuant to section 110(k), the SIP
must not have partial approval, disapproval, or conditional approval of
submittals. EPA is not partially approving, disapproving, nor
conditionally approving any of the SIP actions contained in the June
26, 2001, rule vacated by the Court. EPA is fully approving the
measures submitted by Missouri which are applicable for purposes of
section 107(d)(3)(E)(v), and is determining that the other submissions
are not applicable.
Therefore, the SIP is ``fully approved'' for all applicable
requirements.
Comment 9: EPA attempted to assert that the Missouri and Illinois
SIPs ``can be considered to be approved.'' This is a ``pseudo-
approval'' and an attempt by EPA to escape the simple straightforward
statutory requirement to have a fully approved SIP. This effort by EPA
fails because of the clear language of the CAA, and because EPA must do
a rulemaking to approve the SIP. EPA is also avoiding the requirement
for judicial review of its actions.
Response 9: This comment refers to both the Missouri and Illinois
portions of the St. Louis area. EPA is hereby providing a response
regarding the Missouri portion of the St. Louis area. See the
rulemaking in today's Federal Register regarding redesignation of the

[[Page 25426]]

Illinois portion of the St. Louis area for EPA's response to this
comment as it pertains to the Illinois portion of the St. Louis area.
The use of the phrase ``can be considered to be approved'' (see the
January 30, 2003, proposed rule at 68 FR 4851, 4852) was merely a
statement the SIPs will meet the section 110 requirements and as such
``can be considered to be approved'' if EPA were to approve certain
plan elements, described in the proposed rulemakings. On January 30,
2003, EPA published two proposed rules found at 68 FR 4842 and 68 FR
4847. As part of these proposals, EPA proposed to approve revisions to
Missouri's I/M rule. In today's Federal Register, EPA is taking final
action approving Missouri's I/M rule. By taking these actions, EPA now
concludes that Missouri's SIP is approved. The use of the quoted phrase
was not intended to escape a statutory requirement. In fact, it
recognized EPA's obligation to complete rulemakings in order to approve
SIPs, and it recognized that EPA could not determine that the SIP was
fully approved until it took final action to approve the remaining SIP
elements. All of the SIP elements which are applicable to the St. Louis
area for purposes of redesignation have either been approved in
previous rulemakings (see response to comments 6, 7, 8, 13, 14, 15, and
16 for a discussion of these prior rulemakings) or are approved in
rulemakings published today.
The proposed rule at 68 FR 4851 states that on November 25, 2002,
the U.S. Court of Appeals for the Seventh Circuit (Court) issued a
decision in Sierra Club and Missouri Coalition for the Environment v.
EPA, 311 F. 3d 853 (7th Cir. 2002). In this decision, the Court vacated
the June 26, 2001, rule and remanded to EPA for entry of a final rule
that reclassifies St Louis as a serious nonattainment area for ozone.
Although the Court's opinion addressed only EPA's action extending the
attainment date for St. Louis, the Court's order vacated the other EPA
actions in the rulemaking as well. EPA has approved all SIP elements
that are applicable to the St. Louis area and is determining that
certain others are not applicable. This is not a ``pseudo-approval'' of
the SIP elements, but a determination that because certain requirements
(e.g., the attainment demonstration and RACM) are not applicable, they
need not be approved. (See response to comment 8 for more discussion of
the requirement for a fully approved SIP.) The applicable requirements
which were approved prior to the June 26, 2001, action (e.g., VOC RACT,
NO_X RACT, the ROP Plan) were subject to notice and comment
rulemaking and judicial review. The measures approved today (the
maintenance plan and contingency measures, MVEBs, I/M program
revisions) have been subject to notice and comment rulemaking and EPA's
action is subject to judicial review. EPA's determination that certain
requirements are not applicable has been subject to notice and comment
rulemaking and is subject to judicial review. The public has had full
opportunity to comment on all of EPA's actions, as evidenced by the
numerous comments submitted by the commenter. Therefore, EPA has not
avoided any requirement for public comment or judicial review.
In acting upon a redesignation request, EPA may rely on any prior
SIP approvals plus any additional approvals it may perform in
conjunction with acting on the redesignation. EPA has already taken
final action to approve all required SIP elements or is approving them
in conjunction with this final action on the redesignation. Therefore,
the St. Louis area has a fully approved SIP. See ``Procedures for
Processing Requests to Redesignate Areas to Attainment,'' John
Calcagni, Director, Air Quality Management Division, September 4, 1992,
page 3 (Calcagni memo). The Calcagni memo allows for approval of SIP
elements and redesignation to occur simultaneously, and EPA has
frequently taken this approach in its redesignation actions. See (66 FR
53096) (Pittsburgh-Beaver Valley, Pennsylvania, October 19, 2001); (65
FR 37879) (Cincinnati-Hamilton, Ohio, June 19, 2000); (61 FR 20458)
(Cleveland-Akron-Lorain, Ohio May 7, 1996); (60 FR 37366) (July 20,
1995), (61 FR 31832-31833) (June 21, 1996) (Grand Rapids, MI).
Comment 10: The SIPs fail to meet the section 110 requirements
because the ``inapplicable ``moderate'' area'' requirements contained
in the SIPs do not provide for implementation, maintenance, and
enforcement of the NAAQS because modeling shows that the plan does not
provide for attainment until 2004. Furthermore, Missouri has failed to
meet the section 110(a)(2)(D) requirements related to the
NO_X SIP call.
Response 10: EPA finds that the Missouri SIP meets the section 110
requirements. See the January 30, 2003, proposal and the responses to
comments 8 and 9 for further discussion.
Submissions under the NO_X SIP call are not applicable
requirements for purposes of evaluating a redesignation request.
At this time, Missouri is not subject to the NO_X SIP
call. As explained in the proposal, EPA's determination that Missouri
significantly contributes to downwind nonattainment was vacated by the
Court of Appeals for the District of Columbia Circuit. EPA is not
relying on a SIP to predict attainment but is relying on air quality
monitoring data to show that the area has attained. With respect to the
assertion that the area must have an approved attainment demonstration
SIP in order to meet the requirements of section 110, EPA has addressed
this issue in its response to comments on the lack of an approved
attainment demonstration for the area. Section 110(a)(1) does not add
any additional requirements for compliance with the NAAQS other than
those included in section 172(c) and 182, and the commenter does not
identify any specific additional requirements. See the responses to
comments 3, 21, and 24 with respect to the assertion that the modeling
for the area shows that it cannot attain until 2004.
The SIP call budget for Missouri was proposed on February 22, 2002
(67 FR 8396), but has not yet been finalized. For this reason alone, it
is not an applicable requirement. In addition, the NO_X SIP
call requirements for a state are not linked with a particular
nonattainment area's designation and classification in that state. EPA
believes that the requirements linked with a particular nonattainment
area's designation and classification are the relevant measures to
evaluate in reviewing a redesignation request. The NO_X SIP
call submittal requirements, where applicable, continue to apply to a
state regardless of the designation of any one particular area in the
state.
Thus, we do not agree that the NO_X SIP call submission
should be construed to be an applicable requirement for purposes of
redesignation. The section 110 and part D requirements, which are
linked with a particular area's designation and classification, are the
relevant measures to evaluate in reviewing a redesignation request.
This policy is consistent with EPA's existing conformity and oxygenated
fuels requirements, as well as with section 184 ozone transport
requirements. See Reading, Pennsylvania, proposed and final rulemakings
(61 FR 53174-53176, October 10, 1996), (62 FR 24826, May 7, 1997);
Cleveland-Akron-Lorain, Ohio, final rulemaking (61 FR 20458, May 7,
1996); and Tampa, Florida, final rulemaking at (60 FR 62748, December
7, 1995). See also the discussion on this issue in the Cincinnati
redesignation (65 FR 37890, June 19, 2000), and in the

[[Page 25427]]

Pittsburgh redesignation (66 FR 50399, October 19, 2001).
Comment 11: The state SIPs fail to meet the part D requirements of
the CAA. EPA asserts that certain requirements of part D are not
applicable because monitoring data shows the area has attained. EPA
relies on the case of Sierra Club v. EPA for this conclusion. However,
this case has no application here because it was not a ``redesignation
case.'' Given the attainment demonstration modeling, it would be
impossible to conclude that any of the ``part D requirements are not
necessary.'' All part D requirements are applicable unless, prior to
redesignation, EPA formally exempts the St. Louis area from the part D
requirements.
Response 11: Section II.A of this document, discussing the
rationale for EPA's determination of attainment and suspension of
certain requirements, addresses the applicability of the part D
requirements. The part D requirements specifically include the
requirements of sections 172(c) and 176 as well as the applicable
requirements of subpart 2. The section 172(c) requirements include
General Plan Requirements which to the extent applicable, must provide
for the implementation of all RACM as expeditiously as practicable (at
a minimum this requires RACT for stationary source), RFP, emissions
inventory, identification and quantification of allowable emissions for
major new or modified stationary sources, permits for new and modified
major stationary sources, other emission control measures needed to
assure attainment of the NAAQS, section 110(a)(2) requirements, and
contingency measures. Section 110(a)(2) requirements include submittal
of a SIP that has been adopted by the state after reasonable public
notice and hearing; provisions for establishment and operation of
appropriate apparatus, methods, systems, and procedures needed to
monitor ambient air quality; implementation of a source permit program;
provisions for the implementation of part C requirements (Prevention of
Significant Deterioration (PSD)); provisions for the implementation of
part D requirements (nonattainment area NSR permit programs);
provisions for stationary source emission control measures, source
monitoring, and source reporting; provisions for air pollution
modeling; and provisions for public and local agency participation in
planning and emission control rule development. Subpart 2 requirements
include attainment demonstration, 1990 base year inventory and periodic
emissions inventories updates, emission statements, rate-of-progress
plans, VOC RACT, RACM, stage II vapor recovery, I/M, and NO_X
emission controls.
As stated in the response to comment 8 above, the Missouri SIP
meets all applicable requirements including section 110 and part D
requirements. As stated in the January 30, 2003, proposed rule at 68 FR
4852 and 4853, EPA has approved each state's RFP, permitting programs,
and VOC RACT rules as meeting the requirements of part D. Missouri's
SIP has regulations requiring annual emission statements from major
sources. Missouri has submitted complete emission inventories. Missouri
has approved general conformity rules pursuant to section 176. In
addition, Missouri has approved transportation conformity rules. EPA is
approving in this action Missouri's maintenance plan which includes
adequate contingency measures. Thus, Missouri has met the applicable
part D requirements of the CAA. Note that also as stated in the
response to comment 8, by finding that the St. Louis area has attained
the standard, the attainment demonstration and RACM requirements are no
longer applicable requirements. See also the final rule for Illinois
describing how the Metro-East St. Louis area has met the applicable
requirements.
As indicated in comment 3 above, neither section 107(d)(3)(E) nor
EPA policy referenced by the commenter requires modeling as a
prerequisite to redesignation of an ozone nonattainment area. In
addition, no modeling was conducted as part of the redesignation
requests submitted by Missouri or Illinois. Thus, there is no modeling
basis for EPA to make any conclusions regarding the necessity for the
part D requirements. (Modeling is not a required element of a
redesignation request. See, 65 FR 37879--Cincinnati redesignation for
additional discussion of this issue. See, Wall v. EPA, 265 F.3d. 426
upholding this interpretation.) However, as explained in detail in
comment 3, the monitoring data collected over the 2000 through 2002
period show that the area has in fact attained the ozone standard. EPA
finds no need for further controls to bring about attainment.
With respect to the commenter's assertion that the Tenth Circuit
Sierra Club case is not applicable because it is not a
``redesignation'' case, the commenter misses the point of the case as
it relates to St. Louis. The Tenth Circuit's endorsement of the
interpretation of the CAA in the Seitz memo (that certain ``statutory''
requirements relating to attainment are not applicable to an area which
has attained the standard) was not dependent on the fact that the area
was not being redesignated. The case involved a determination by EPA
that Salt Lake and Davies Counties, Utah, had attained the standard,
and that, therefore, certain additional requirements relating to
attainment (such as an attainment demonstration) would not apply so
long as the area continued to attain. The Court expressly recognized
that the area could be redesignated without having met those
requirements, even though the action at issue there was an attainment
determination and not a redesignation. The Court stated: ``Recall that
the Environmental Protection Agency's determination to exempt the
Counties from limited ozone requirements is really no more than a
suspension of those requirements for so long as the area continues to
attain the standard or until the area is formally redesignated to
attainment.'' (Sierra Club v. EPA, 99 F.3d 1551, 1558 (10th Cir.
1996)). (See also, 66 FR 53095 for EPA's redesignation of the
Pittsburgh area.) The Court did not say, as the commenter would have
it, that the area would have to adopt those measures which had been
determined to be unnecessary in order to be redesignated. As it did for
the Utah counties, in which EPA redesignated those counties without
requiring that they meet the suspended requirements, EPA is here
determining that the St. Louis area is attaining the standard and that
certain requirements are suspended and do not apply because the area is
being redesignated. The basis for this determination and the suspension
of certain requirements for the area was explained in detail in the
proposal found at 68 FR 4850-4858 and further explained in this
response to various comments on the issue. The determination is based
on monitored data, not modeling, for reasons explained in this
document. Nothing in the Tenth Circuit case prohibits EPA from
simultaneously suspending the requirements and redesignating an area,
which is what this rulemaking accomplishes. EPA has taken this dual
action in a number of areas including Louisville (66 FR 53665),
Cincinnati (65 FR 37879), Grand Rapids (61 FR 31831), and Pittsburgh
(66 FR 53094). Upon redesignation to attainment, the suspended
nonattainment area requirements will no longer apply at all since the
area is no long a designated nonattainment area.
Comment 12: EPA asserts that the RACM requirements of section
172(c)(1) need not be adopted because the area has attained the NAAQS,
thus, these

[[Page 25428]]

measures would not accelerate attainment. This is confoundingly
circular reasoning which erases the ``fully approved'' requirements of
the CAA. EPA's assertion is not relevant here.
Response 12: The April 16, 1992, General Preamble (57 FR 13560)
states that EPA interprets section 172(c)(1) such that the RACM
requirements are a ``component'' of an area's attainment demonstration.
Thus, since the attainment demonstration is not an applicable
requirement, RACM is also no longer an applicable requirement. See
response to comment 8 for further discussion. Also, EPA has been
consistent in this interpretation. See the final rulemaking for
Pittsburgh, 66 FR 53096 (October 19, 2001) for additional discussion of
this interpretation.
EPA believes that its policy is not ``confoundingly circular
reasoning'' but rather straightforward reasoning. It is reasonable to
conclude that states need not develop an attainment demonstration
showing how they will attain a NAAQS that they have already attained.
Similarly, states need not adopt additional reasonably available
control measures as necessary to accelerate attainment when attainment
has already been achieved.
As stated in the response to comments 8 and 9, SIPs must be ``fully
approved'' as required by section 107(d)(3)(E)(ii), only with respect
to the ``applicable'' requirements of section 110 and part D, as
addressed in section 107(d)(3)(E)(v). If requirements are not
``applicable'' with respect to those sections, they need not be fully
approved.
Comment 13: The RACM and RACT requirements of the CAA are not tied
to reasonable further progress but are required by the CAA to be
implemented as expeditiously as practicable. This is supported by H.R.
Rep. No. 101-490, Part 2, 101st Cong., 2d Sess. at p. 223; Sierra Club
v. EPA, 99 F.3d 1551, 1557 (10th Cir. 1996); Wall v. EPA, 265 F.3d 426,
441 (6th Cir. 2001); and, EPA's Seitz memo, page 4. EPA's contention
that any additional RACM and RACT measures need not be adopted directly
repudiates the plain language of the CAA.
Response 13: This comment refers to both the Missouri and Illinois
portions of the St. Louis area. EPA is hereby providing a response
regarding the Missouri portion of the St. Louis area. See the
rulemaking in today's Federal Register regarding redesignation of the
Illinois portion of the St. Louis area for EPA's response to this
comment as it pertains to the Illinois portion of the St. Louis area.
EPA has previously addressed the rationale for its determination
that additional RACM is not required for an area attaining the
standard. (See, e.g., section II and response to comment 12.) The RFP
requirement under section 172(c)(2) is defined as progress that must be
made toward attainment. Section 182(b)(1)(A) sets forth the specific
requirements for RFP for a moderate nonattainment area which includes a
reduction in VOC emissions of at least 15 percent from baseline
emissions. As stated in the January 30, 2003, proposed rule at 68 FR
4854, 4855, EPA approved Missouri's 15 percent ROP plan.
RACM is a general requirement of section 172(c)(1) which calls for
SIPs to contain ``all reasonably available control measures as
expeditiously as practicable (including such reductions in emissions
from existing sources in the area as may be obtained through the
adoption, at a minimum, of reasonably available control technology and
shall provide for attainment of the national primary ambient air
quality standards.'' EPA has consistently interpreted this provision to
require only implementation of potential RACM measures that could
contribute to reasonable progress or attainment. (See General Preamble
57 FR 13498, April 16, 1992.) Thus, where an area has already met all
applicable requirements for progress and has attained the relevant
standard, no additional RACM measures are required.
Section 182(b)(2) specifies the SIP requirements for RACT in
moderate nonattainment areas. These requirements include implementation
of RACT at each source of VOCs covered by Control Technology Guidelines
(CTGs) and all other major sources of VOCs. EPA has never indicated
that the area could avoid implementing VOC RACT requirements because
the area has attained the standard.
As stated in the January 30, 2003, proposed rule at 68 FR 4855,
Missouri has adopted and implemented all required VOC RACT rules. In
addition, section 182(f) establishes NO_X RACT requirements
for major stationary sources. EPA approved Missouri's NO_X
RACT rule into the SIP on May 18, 2000 (65 FR 31482).
The commenter states that H.R. Rep. No. 101-490, Part 2, 101st
Cong., 2d Sess. at p. 223 does not tie RACM and RACT measures to RFP.
This document is a recitation of the statute, but does not address
tying RACM and RACT to RFP.
With respect to the commenter's contention that EPA's position
regarding additional RACM and RACT measures was rejected in the Tenth
Circuit Sierra Club case and in Wall, the commenter is incorrect. The
Wall case involved VOC RACT, which is not an issue here, because, as
discussed previously, and in response to comment 14 below, Missouri has
adopted all applicable VOC RACT measures. Missouri has also adopted
NO_X RACT measures. The Tenth Circuit Sierra Club case upheld
EPA's determination that RACT was not tied to reasonable further
progress, and that case did not address EPA's interpretation of RACM at
all. The commenter's Seventh Circuit brief, which it relies on to
support its position that RACM requirements must be met for an area to
be redesignated, argued that EPA's interpretation of the RACM
requirement (that section 172(c)(1) requires only implementation of all
RACM which would expedite attainment) is an improper reading of the
CAA. That issue was not addressed or decided by the Seventh Circuit.
However, the issue of EPA's interpretation of the RACM requirement was
raised and upheld in the 5th Circuit (Sierra Club v. EPA, 314 F.3d 735,
743-745 (5th Cir. 2002)) and the District of Columbia Circuit (Sierra
Club v. EPA, 294 F.3d 155, 162-163 (D.C. Cir. 2002)). Both circuits
found that EPA's interpretation that the statute only required
implementation of RACM measures that would advance attainment was
reasonable.
Comment 14: The rulemaking should identify each VOC RACT rule
implemented by the states and identify whether the states have met the
VOC RACT requirements.
Response 14: This comment refers to both the Missouri and Illinois
portions of the St. Louis area. EPA is hereby providing a response
regarding the Missouri portion of the St. Louis area. See the
rulemaking in today's Federal Register regarding redesignation of the
Illinois portion of the St. Louis area for EPA's response to this
comment as it pertains to the Illinois portion of the St. Louis area.
The January 30, 2003, proposed rule states at 68 FR 4855 that both
states have adopted and implemented all required VOC RACT rules. In
addition, the proposed rule provided the following web sites which
contain the content of these rules, and references to EPA's rulemakings
approving these rules. The Web site for Missouri is: http://www.epa.gov/
region07/programs/artd/air/rules/missouri/chap5.htm.
The VOC RACT rules listed on this Web site and EPA's rulemakings
approving these rules include the following:

10 CSR 10-5.070 Open Burning Restrictions, 37 FR 10842 (5/31/72)

[[Page 25429]]

10 CSR 10-5.220 Control of Petroleum Liquid Storage, Loading and
Transfer, 37 FR 10842 (5/31/72)
10 CSR 10-5.295 Control of Emissions From Aerospace Manufacturing and
Rework Facilities, 65 FR 31489 (5/18/2000)
10 CSR 10-5.300 Control of Emissions from Solvent Metal Cleaning, 45 FR
24140 (4/9/80) and 45 FR 56806 (7/11/80) (correction)
10 CSR 10-5.310 Liquefied Cutback Asphalt Paving Restricted, 45 FR
24140 (4/9/80) and 45 FR 46806 (7/11/80) (correction)
10 CSR 10-5.320 Control of Emissions from Perchloroethylene Dry
Cleaning Installations, 46 FR 20172 (4/3/81)
10 CSR 10-5.330 Control of Emissions from Industrial Surface Coating
Operations, 45 FR 24140 (4/9/80) and 45 FR 46806 (7/11/80) (correction)
10 CSR 10-5.340 Control of Emissions from Rotogravure and Flexographic
Printing Facilities, 46 FR 20172 (4/3/81)
10 CSR 10-5.350 Control of Emissions from Manufacture of Synthesized
Pharmaceutical Products, 46 FR 20172 (4/3/81)
10 CSR 10-5.360 Control of Emissions from Polyethylene Bag Sealing
Operations, 49 FR 40164 (10/15/84)
10 CSR 10-5.370 Control of Emissions from the Application of Deadeners
and Adhesives, 55 FR 7712 (3/5/90)
10 CSR 10-5.390 Control of Emissions from Manufacture of Paints,
Varnishes, Lacquers, Enamels and Other Allied Surface Coating Products,
50 FR 14925 (4/16/85)
10 CSR 10-5.410 Control of Emissions from the Manufacture of
Polystyrene Resin, 55 FR 7712 (3/5/90)
10 CSR 10-5.420 Control of Equipment Leaks from Synthetic Organic
Chemical and Polymer Manufacturing Plants, 53 FR 12417 (4/14/88)
10 CSR 10-5.440 Control of Emissions from Bakery Ovens, 65 FR 8060 (2/
17/2000)
10 CSR 10-5.442 Control of Emissions From Offset Lithographic Printing
Operations, 65 FR 8060 (2/17/00)
10 CSR 10-5.450 Control of VOC Emissions from Traffic Coatings, 65 FR
8060 (2/17/00)
10 CSR 10-5.451 Control of Emissions from Aluminum Foil Rolling, 65 FR
8060 (2/17/00)
10 CSR 10-5.455 Control of Emissions from Solvent Cleanup Operations,
65 FR 8060 (2/17/00)
10 CSR 10-5.490 Municipal Solid Waste Landfills, 63 FR 20320 (4/24/98)
10 CSR 10-5.500 Control of Emissions From Volatile Organic Liquid
Storage, 65 FR 31489 (5/18/00)
10 CSR 10-5.520 Control of Volatile Organic Compound Emissions From
Existing Major Sources, 65 FR 31489 (5/18/2000)
10 CSR 10-5.530 Control of Volatile Organic Compound Emissions From
Wood Furniture Manufacturing Operations, 65 FR 31489 (5/18/00)
10 CSR 10-5.540 Control of Emissions From Batch Process Operations, 65
FR 31489 (5/18/00)
10 CSR 10-5.550 Control of Volatile Organic Compound Emissions From
Reactor Processes and Distillations Operations Processes in the
Synthetic Organic Chemical Manufacturing Industry, 65 FR 31489 (5/18/00)
The rationale for approval of each of these rules is described in
the respective Federal Register document approving each rule. As stated
previously, in the response to comment 5, this redesignation rulemaking
does not reopen rulemakings regarding prior SIP approvals.
Comment 15: Missouri has not adopted all appropriate NO_X
and NO_X RACT rules. Thus, the SIP is not approvable.
Response 15: Missouri has adopted and EPA has approved into
Missouri's SIP a NO_X RACT rule meeting the requirements of
section 182(f). The Missouri NO_X RACT rule can be found at
10 CSR 10-5.510. See comment 13 for further discussion on Missouri's
NO_X RACT rule. As described in response to previous
comments, pursuant to the Calcagni Memo page 3, and upheld in the Wall
case cited previously, an EPA action on a redesignation request does
not mean that earlier issues with regard to the SIP will be reopened.
See also, Southwestern Pennsylvania Growth Alliance v. Browner, 144
F.3d 984 (6th Cir. 1998). Thus, EPA is not reopening Missouri's
NO_X RACT rule as part of this redesignation.
Missouri has adopted and EPA has approved into the SIP a state-wide
NO_X rule (10 CSR 10-6.350 Emissions Limitations and
Emissions Trading of Oxides of Nitrogen, 65 FR 82285 (12/28/00)).
As stated in comment 10 above, EPA believes that submissions under
the NO_X SIP call are not applicable requirements for
purposes of evaluating Missouri's redesignation request.
EPA has determined that Missouri has adopted all applicable
NO_X and NO_X RACT rules.
Comment 16: The Missouri I/M rule being approved in a separate
rulemaking does not meet the requirements for an I/M program. EPA needs
to explain how it can approve an I/M rule since it does not meet the I/
M requirements for a serious area.
Response 16: EPA is responding to comments regarding Missouri's I/M
program in a separate rulemaking published in today's Federal Register.
EPA's response to comments included in that rulemaking are incorporated
here.
The Federal rule at 40 CFR 51.372(c) states that ``Any
nonattainment area that EPA determines would otherwise qualify for
redesignation from nonattainment to attainment shall receive full
approval of a SIP submittal under Sections 182(a)(2)(B) or 182(b)(4) if
the submittal contains the following elements: (1) Legal authority to
implement a basic I/M program (or enhanced if the State chooses to opt
up) as required by this subpart. The legislative authority for an I/M
program shall allow the adoption of implementing regulations without
requiring further legislation. (2) A request to place the I/M plan (if
no I/M program is currently in place or if an I/M program has been
terminated) or the I/M upgrade (if the existing I/M program is to
continue without being upgraded) into the contingency measures portion
of the maintenance plan upon redesignation. (3) A contingency measure
consisting of a commitment by the Governor or the Governor's designee
to adopt or consider adopting regulations to implement the required I/M
program to correct a violation of the ozone or CO standard or other air
quality problem, in accordance with the provisions of the maintenance
plan. (4) A contingency commitment that includes an enforceable
schedule for adoption and implementation of the I/M program, and
appropriate milestones. The schedule shall include the date for
submission of a SIP meeting all of the requirements of this subpart.
Schedule milestones shall be listed in months from the date EPA
notifies the State that it is in violation of the ozone or CO standard
or any earlier date specified in the State plan. Unless the State, in
accordance with the provisions of the maintenance plan, chooses not to
implement I/M, it must submit a SIP revision containing an I/M program
no more than 18 months after notification by EPA.''
Regarding item (1) above, as indicated in the response to comment
35, Missouri has the authority to implement an I/M program. Regarding
item (2) above, the maintenance plan contains ``High Enhanced I/M'' as
a contingency measure. The plan was accompanied by a request from an
authorized Missouri official for EPA to approve the maintenance plan.
Regarding item (3) above, section 7.1 of the maintenance plan contains
a commitment to adopt or consider adopting the I/M program listed as a
contingency measure.

[[Page 25430]]

Regarding item (4) above, the SIP contains an enforceable schedule for
adoption and implementation of the I/M program. Section 7.1 of the
maintenance plan sets for a schedule with milestones for promulgation
and implementation of a program meeting the requirements.
This meets the condition imposed by the Federal rule at 40 CFR
51.372(c). Thus, EPA is approving the I/M program in a separate
rulemaking. This satisfies the basic I/M requirements for moderate
ozone areas. Since EPA is taking final action to approve the
redesignation of the St. Louis area prior to the date that the serious
area requirement for enhanced I/M would be due, EPA can approve the I/M
program as meeting the moderate rather than the serious area I/M
requirement, as fully explained in this final rule and in the separate
I/M approval action taken elsewhere in today's Federal Register.

D. Comments Related to Criterion 3: The Improvement in Air Quality Must
Be Due to Permanent and Enforceable Reductions in Emissions

Comment 17: The area cannot meet this requirement since there is
not an approved SIP meeting the ``serious'' area requirements, and
there is no applicable implementation plan.
Response 17: This comment refers to both the Missouri and Illinois
portions of the St. Louis area. EPA is hereby providing a response
regarding the Missouri portion of the St. Louis area. See the
rulemaking in today's Federal Register regarding redesignation of the
Illinois portion of the St. Louis area for EPA's response to this
comment as it pertains to the Illinois portion of the St. Louis area.
As described in the response to comments for Criterion 2 above, the
SIPs meet the applicable CAA requirements. The applicable SIP
requirements are described in the January 30, 2003, proposed rulemaking
(68 FR 4850-4856). EPA's approval of previous SIP submittals, this
rulemaking and today's rulemaking approving Missouri's I/M rule render
Missouri's SIP ``fully approved'' for all applicable SIP requirements.
As stated in response to comments relating to Criterion 2, above, since
the serious area requirements are not yet due, the SIP is not deficient
because the serious area requirements have not been included.
In any event, this criterion is not dependent on which requirements
are applicable or have been approved or implemented. The requirement is
that air quality improvements be attributable to permanent and
enforceable reductions in emissions which is a separate inquiry from
the question of the requirements applicable to the area. Missouri's
submission contains a detailed analysis of the air quality improvements
in St. Louis and their relation to the permanent and enforceable
control measures which are in place in the area. (See response to
comment 19 for further discussion.) These measures are listed in the
proposal at 68 FR 4856-4858. These measures are all part of the
applicable SIP. Thus, the commenter is incorrect in its assertion that
there is no applicable SIP.
Comment 18: It is impossible to demonstrate that monitored
concentrations on the 2002 Labor Day weekend resulted from permanent
and enforceable reductions. The reductions were due to voluntary
curtailment of operations by large industrial operations.
Response 18: The monitoring data for the St. Louis nonattainment
area demonstrate that the estimated number of exceedances per year
averaged over three years is 1.0 or less at all monitoring sites in the
area. EPA believes that any voluntary measures taken by industry and
others over a two-or three-day period in this three-year time period
does not render the air quality monitoring data unrepresentative of the
air quality. As explained in more detail in response to comment 19
below, ozone levels monitored during 2000-2002 are due to permanent and
enforceable measures which are in place (e.g., I/M programs, RACT on
VOC and NO_X stationary sources).
In the event that some sources did voluntarily reduce emissions
over this two- or three-day period, EPA has no basis to conclude that
these voluntary reductions had an effect on the monitored air quality.
As the commenter points out, ozone formation occurs through ``complex
chemistry and meteorology.'' Voluntary reductions over a short time
period may or may not have had an impact on the monitored air quality.
(We note that ``voluntary'' reductions are always a factor, since total
emissions at a given point in time depend, for example, on how many
people decide to drive on a given day or weekend.) However, the state's
demonstration that air quality improvements are due to permanent and
enforceable emission reductions is based on its analysis of emission
reductions over a ten-year period (see response to comment 19),
consistent with the CAA requirements and EPA policy including the
Calcagni memo at page 4. Also, see the response to comment 2 above for
further discussion on this issue. Note that in general, EPA encourages
voluntary reductions to reduce emissions. EPA supports programs such as
the Air Quality Index which encourages people to voluntarily reduce
ozone forming activities such as filling gas tanks, painting, mowing,
etc. at times when ozone formation is expected to be high. Although
these measures are not enforceable nor measurable, they are encouraged.
Comment 19: EPA cannot demonstrate that permanent and enforceable
reductions are responsible for any alleged improvement of air quality.
The only way to demonstrate this point is through photochemical grid
modeling. No such modeling has been presented. Without modeling, EPA's
claim is pure speculation. Emission reductions attributable to the
emission controls ``could just as easily lead to increases in ozone
concentrations.'' The attainment demonstration modeling shows that
attainment was ``impossible'' in 2003.
Response 19: This comment refers to both the Missouri and Illinois
portions of the St. Louis area. EPA is hereby providing a response
regarding the Missouri portion of the St. Louis area. See the
rulemaking in today's Federal Register regarding redesignation of the
Illinois portion of the St. Louis area for EPA's response to this
comment as it pertains to the Illinois portion of the St. Louis area.
EPA's response to this and other comments on the attainment
demonstration modeling is included in the response to comments 21 and
24. In addition, see the response to comment 23 for further discussion
regarding the use of modeling in demonstrating maintenance of the NAAQS.
Neither Section 107(d)(3)(E)(iii) nor the Calcagni memo referenced
by the commenter require modeling as a prerequisite to redesignation of
an ozone nonattainment area. Thus, modeling is not required to
demonstrate that the improvement in air quality is due to permanent and
enforceable reductions. See General Preamble for the Interpretation of
Title I of the CAA Amendments of 1990 at 57 FR 13496 (April 16, 1992),
supplemented at 57 FR 18070 (April 28, 1992); ``Procedures for
Processing Requests to Redesignate Areas to Attainment,'' John
Calcagni, Director, Air Quality Management Division, September 4, 1992;
``State Implementation Plan (SIP) Requirements for Areas Submitting
Requests for Redesignation to Attainment of the Ozone and Carbon
Monoxide (CO) National Ambient Air Quality Standards (NAAQS) on or
after November 15, 1992,'' Michael H.

[[Page 25431]]

Shapiro, Acting Assistant Administrator for Air and Radiation,
September 17, 1993; and ``Use of Actual Emissions in Maintenance
Demonstrations for Ozone and CO Nonattainment Areas,'' D. Kent Berry,
Acting Director, Air Quality Management Division, November 30, 1993.
Our guidance provides that an area may meet this requirement by showing
how its ozone precursor emissions changed due to permanent and
enforceable emissions reductions from when the area was not monitoring
attainment of the 1-hour ozone NAAQS to when it reached attainment. See
the rationale set forth in the Cincinnati redesignation (65 FR 37879,
37886-37889, June 19, 2000) and the Pittsburgh redesignation (66 FR
53094, October 19, 2001). The Sixth Circuit has recently upheld EPA's
interpretation in Wall v. EPA (265 F.3d 426, 435).
In the January 30, 2003, proposed rule at 68 FR 4856-4858, EPA
explained the basis for concluding that the observed air quality
improvements are due to the implementation of permanent and enforceable
emission reductions. The reasons include, analysis of the emission
controls which have resulted in emission reductions, an analysis of
meteorological conditions showing a trend toward the reduction of ozone
concentrations while the number of days conducive to forming ozone
showed no significant trend, and an assessment of emissions in 1990 and
2000 which have shown a substantial decrease in emissions of VOCs and
NO_X.
Annual days conducive to ozone formation (those days with
relatively clear skies, low wind speeds and southerly wind directions,
high peak temperatures exceeding 85 degrees Fahrenheit, and little or
no precipitation) have shown no noticeable trend up or down, only
yearly variations. The number of conducive days have stayed between
approximately 20 and 50 days per year with no increasing or decreasing
trend. Meanwhile, exceedances have decreased from over 120 in 1978,
over 100 in 1983, over 60 in 1988, to a total of 11 in the three-year
period of 2000 to 2002. In addition, year-to-year fluctuation of
conducive days cannot be correlated with higher or lower exceedance
levels over the last few years. Since 1989, as the number of conducive
days fluctuated from year to year, the number of exceedances
demonstrated no similar trend. This indicates a disassociation between
monitored exceedances and meteorological effects.
During the 1990-2000 period, as the area-wide ozone design values
in the St. Louis area were decreasing, the VOC and NO_X
emissions in the St. Louis area were also significantly decreasing (see
response to comment 20 for further discussion on the area's design
values). The following tables list VOC and NO_X emissions in
1990 and 2000 for the Missouri and Illinois portions of the St. Louis
ozone nonattainment area. These tables show that the entire
nonattainment area experienced a downward trend in VOC and
NO_X emissions. This downward trend in emissions and ozone
design values, along with no significant trend in the number of days
conducive to ozone formation shows that the observed improvements in
air quality are due to the implementation of permanent and enforceable
emission control measures.

1990 and 2000 Missouri Portion of the St. Louis Nonattainment Area VOC
and NO_X Emissions
[Emissions in tons per ozone season weekday]
------------------------------------------------------------------------
Source category VOC NO_X
------------------------------------------------------------------------
1990
------------------------------------------------------------------------
Point Sources 81.97 347.61
Area Sources 87.74 29.47
On-Road Mobile Sources 135.42 135.00
Off-Road Mobile Sources 64.30 114.32
----------
1990 Totals 369.43 626.40
-------------------------------------------------------
2000
------------------------------------------------------------------------
Point Sources 46.59 165.96
Area Sources 57.38 32.27
On-Road Mobile Sources 103.79 181.75
Off-Road Mobile Sources 40.59 73.16
----------
2000 Totals 248.35 453.14
------------------------------------------------------------------------

1990 and 2000 Metro-East Area VOC and NO_X Emissions
[Emissions in tons per ozone season weekday]
------------------------------------------------------------------------
Source category VOC NO_X
------------------------------------------------------------------------
1990
------------------------------------------------------------------------
Point Sources 74.05 95.85
Area Sources 33.84 1.66
On-Road Mobile Sources 43.27 45.13
Off-Road Mobile Sources 23.49 23.99
----------
1990 Totals 174.65 166.63
-------------------------------------------------------
2000
------------------------------------------------------------------------
Point Sources 17.91 61.91
Area Sources 28.32 1.18
On-Road Mobile Sources 26.57 54.71
Off-Road Mobile Sources 21.31 23.85
----------
2000 Totals 94.11 141.64
------------------------------------------------------------------------

Reductions in ozone precursor (VOC and NO_X) emissions
have brought many areas across the country into attainment. EPA has
approved many ozone redesignations showing decreases in ozone precursor
emissions resulting in attainment of the ozone standard. See
redesignations for Pittsburgh (66 FR 53094, October 19, 2001),
Cincinnati (65 FR 37879, June 19, 2000), Charleston (59 FR 30326, June
13, 1994; 59 FR 45985, September 6, 1994), Greenbrier County (60 FR
39857, August 4, 1995), Parkersburg (59 FR 29977, June 10, 1994); (59
FR 45978, September 6, 1994), Jacksonville/Duval County (60 FR 41,
January 3, 1995), Miami/Southeast Florida (60 FR 10325, February 24,
1995), Tampa (60 FR 62748, December 7, 1995), Lexington (60 FR 47089,
September 11, 1995), Owensboro (58 FR 47391, September 9, 1993),
Indianapolis (59 FR 35044, July 8, 1994; 59 FR 54391, October 31,
1994), South Bend-Elkhart (59 FR 35044, July 8, 1994; 59 FR 54391,
October 31, 1994), Evansville (62 FR 12137, March 14, 1997; 62 FR
64725, December 9, 1997), Canton (61 FR 3319, January 31, 1996),
Youngstown-Warren (61 FR 3319, January 31, 1996), Cleveland-Akron-
Lorain (60 FR 31433, June 15, 1995; 61 FR 20458, May 7, 1996), Clinton
County (60 FR 22337, May 5, 1995; 61 FR 11560, March 21, 1996),
Columbus (61 FR 3591, February 1, 1996), Kewaunee County (61 FR 29508,
June 11, 1996; 61 FR 43668, August 26, 1996), Walworth County (61 FR
28541, June 5, 1996; 61 FR 43668, August 26, 1996), Point Coupee Parish
(61 FR 37833, July 22, 1996; 62 FR 648, January 6, 1997), and Monterey
Bay (62 FR 2597, January 7, 1997). Most of the areas that have been
redesignated to attainment for the 1-hour ozone standard have continued
to attain it. Areas that are not maintaining the 1-hour ozone standard
have a maintenance plan to bring them back into attainment.
Between 1990 and 2000, area-wide VOC and NO_X emissions
in the St. Louis area decreased by 37 percent and 25 percent,
respectively. In Missouri, the VOC and NO_X emissions during
this time period decreased by 33 percent and 28 percent, respectively.
(See the rulemaking redesignating the Illinois portion of the St. Louis
area published in today's Federal Register for NO_X and VOC
reductions for the Metro-East area.) These emissions reductions were
due to the implementation of Missouri's 15 percent rate-of-progress
plan, including its implementation of a centralized motor vehicle
inspection and maintenance program and stationary source controls.
Additional reductions

[[Page 25432]]

were due to tighter Federal standards for new vehicles, and some were
due to requirements for reformulated and low Reid Vapor Pressure (RVP)
gasoline for motor vehicles. In addition, Title IV of the CAA resulted
in reduced NO_X emissions from utility sources.
The commenter claims that the combination of NO_X and VOC
emissions reductions could just as easily have led to increases in
ozone. However, the actual monitoring data collected in the area shows
that ambient ozone concentrations have dropped when this combination of
ozone precursor reductions occurred. In other metropolitan areas, other
levels of VOC and NO_X reductions have also resulted in
attainment. See the areas listed above in first part of this response.
The St Louis area's decrease in ozone levels is consistent with what
other areas have experienced. The commenter has not provided data
showing that decreases in ozone precursor emissions have led to higher
levels of ozone.
EPA's conclusion that improvements in air quality are attributable
to permanent and enforceable reductions in precursors is not
``speculation'' but is based on a careful review of the various
technical analyses conducted by the states and described above. EPA
believes it is reasonable not to require photochemical grid modeling.
Three-year averaging addresses variations in meteorological conditions,
an analysis of meteorological conditions showed no significant trend in
the number of days conducive to ozone formation, and the commenter has
presented no evidence that the three-year attainment period was
unusually favorable. It is important to note that redesignation is not
intended as an absolute guarantee that the area will never monitor
future violations. This is what maintenance plan contingency measures
are designed to address and correct. See the Cincinnati redesignation
(65 FR 37879, 37886-37889, June 19, 2000) and the Pittsburgh
redesignation (66 FR 53094, October 19, 2001) for additional discussion
of this issue.
Comment 20: If improvements in St. Louis air quality were due to
permanent and enforceable reductions, the trend in monitored
concentrations would be to go down. However, exceedances tripled from
2000 to 2001 and more than doubled from 2001 to 2002.
Response 20: As stated in response to comment 2 above, a violation
of the 1-hour ozone NAAQS occurs when the estimated number of
exceedances per year averaged over three years is greater than 1.0 at
any monitoring site in the area or its downwind environs, using
conventional rounding techniques. Although there was an increase in the
number of exceedances between 2000 and 2001 as well as between 2001 and
2002, year-to-year trends in exceedances are not used to determine
attainment, but rather an average over three years is used. For reasons
stated previously, EPA has determined that the St. Louis area is in
attainment with the NAAQS.
As indicated in the January 30, 2003, proposal at 68 FR 4850, Table
1 Summarizes the number of expected exceedances at each monitor in the area.

Table 1.--1-Hour Ozone NAAQS Exceedances in the St. Louis, Illinois-Missouri Area from 2000 to 2002
----------------------------------------------------------------------------------------------------------------
Estimated exceedances Average number
--------------------------- of estimated
Site name County or city and state exceedances
2000 2001 2002 2000-2002
----------------------------------------------------------------------------------------------------------------
Jerseyville............................. Jersey, IL................. 0.0 1.0 1.0 0.7
Alton................................... Madison, IL................ 0.0 0.0 0.0 0.0
Maryville............................... Madison, IL................ 0.0 0.0 1.0 0.3
Edwardsville............................ Madison, IL................ 0.0 0.0 0.0 0.0
Wood River.............................. Madison, IL................ 0.0 1.0 0.0 0.3
Houston................................. Randolph, IL............... 0.0 0.0 0.0 0.0
East St. Louis.......................... St. Clair, IL.............. 0.0 0.0 0.0 0.0
Arnold.................................. Jefferson, MO.............. 0.0 0.0 0.0 0.0
West Alton.............................. St. Charles, MO............ 1.0 1.0 1.0 1.0
Orchard Farm............................ St. Charles, MO............ 0.0 0.0 2.0 0.7
Bonne Terre............................. St. Genevieve, MO.......... 0.0 0.0 0.0 0.0
South Lindbergh......................... St. Louis, MO.............. 0.0 0.0 2.0 0.7
Queeny.................................. St. Louis, MO.............. 0.0 0.0 0.0 0.0
Hunter.................................. St. Louis, MO.............. 0.0 0.0 0.0 0.0
Flo Valley.............................. St. Louis, MO.............. 0.0 0.0 0.0 0.0
St. Ann (old)........................... St. Louis, MO.............. 0.0 n/a n/a \1\ 0.0
St. Ann (new)........................... St. Louis, MO.............. n/a 0.0 0.0 \1\ n/a
Broadway................................ St. Louis City, MO......... 0.0 0.0 0.0 0.0
Clark................................... St. Louis City, MO......... 0.0 0.0 0.0 0.0
Margaretta.............................. St. Louis City, MO......... 0.0 0.0 0.0 0.0
----------------------------------------------------------------------------------------------------------------
\1\ The owner of the property on which the old St. Ann monitor was located terminated the lease agreement with
the Missouri Department of Natural Resources. The new site is 0.7 miles east of the old site. In general,
ambient monitors should remain at the same location for the duration of the monitoring period required for
demonstrating attainment. However, when three complete, consecutive calendar years of data is not available
for a monitoring site, adjustments are made consistent with EPA monitoring criteria, in determining the
average number of estimated exceedances per year. The average number of estimated exceedances for 2000-2002
for the old St. Ann monitor is the estimated exceedances for 2000, or 0.0. In addition, where a monitor has
been in operation less than three years, the average estimated number of exceedances cannot be determined.
Since the new St. Ann monitor has been in operation less than three years, the average number of estimated
exceedances for 2000-2002 was not determined.

The area has monitored attainment for the three-year period from
2000-2002. This demonstrates that the current level of emissions is
adequate to keep the area in attainment during weather conditions as in
past years associated with higher levels of ozone. In addition, the CAA
does not presume that the area will always be in attainment. The CAA
provides that if the area were to violate the 1-hour ozone standard,
then the contingency measures in the maintenance plan would be
triggered. This would reduce the ozone precursor emissions and bring
the area back into attainment.
One exceedance in the area was monitored in 2000, three in 2001,
and

[[Page 25433]]

seven in 2002. EPA notes that when dealing with numbers as small as one
exceedance in 2000, any subsequent increase in the number of
exceedances will result in the number of exceedances being at least
doubled. In other words, when dealing with a number as small as one,
any increase will be at least double that value. Thus, citing a
doubling or tripling of exceedances is not necessarily an indicator of
significant changes in air quality.
The one-hour ozone NAAQS is based upon a three-year average. For a
violation, the estimated number of exceedances per year must exceed 1.0
at any monitoring site. Under this standard, a monitor may record up to
three exceedances over a three-year period without causing a violation
of the standard. The fourth highest monitored level at a monitor over a
three-year period can be used as an indicator of potential violations
of the NAAQS. (Note that since other factors, such as missing data, can
affect the calculation of the estimated number of exceedances, the
fourth highest monitored value is not solely used to determine a
violation. See the discussion in the January 30, 2003, proposed rule at
68 FR 4849 and 4850 for an example of how the number of estimated
exceedances is determined.) The term ``design value'' is used to refer
to the fourth highest monitored value in a three-year period. For an
individual monitor, the design value is the fourth highest monitored
value in a three-year period. For an area such as the St. Louis area,
the highest of the individual monitor design values over a three-year
period is referred to as the ``area's design value.'' The lower an
area's design value the more likely the area will meet the standard.
Also, an area's design value which decreases over time indicates that
the monitored ozone concentrations are generally lowering and the air
quality is improving.
The St. Louis area's design value reduced as follows: 0.156 parts
per million (ppm) in 1987-1989 (see 52 FR 13385-13386 dated March 18,
1999); 0.136 ppm in 1994-1996 (see 53 FR 15581 dated March 19, 2001);
0.131 ppm in 1996-1998 (see 53 FR 15583 dated March 19, 2001); 0.127
ppm in 1998-2000 (see 53 FR 15584 dated March 19, 2001); and, 0.123 ppm
in 2000-2002.
This indicates that the monitored air quality improved over this
time period.
In the January 30, 2003, proposed rule at 68 FR 4856-4858, and in
the response to comment 19, EPA explains the basis for concluding that
the observed air quality improvements are due to the implementation of
permanent and enforceable emission reductions. The reasons cited
include emission controls which have resulted in emission reductions,
an analysis of meteorological conditions which has shown a trend in the
reduction of ozone from 1989 to the present while the number of days
conducive to forming ozone showed no significant trend, and an
assessment of emissions in 1990 and 2000 which have shown substantial
decreases in emissions of VOCs and NO_X.
Finally, it is noted that the commenter errs in combining the
exceedance data from many monitors and concluding, on the basis of the
exceedance totals that a worsening ozone trend has occurred. Referring
to Table 1 in the January 30, 2003, proposed rule (68 FR 4850)
(repeated above), one can see that many monitors, including the worst-
case monitor at West Alton, show no consistent trend in exceedance
numbers in the 2000-2002 period. The ``sudden'' increase in exceedances
from zero to two at the Orchard Farm and South Lindbergh monitoring
sites, although implying a worsening ozone trend, simply point to the
instability of considering year-to-year changes within a small time period.
Comment 21: The only modeling which the commenter is aware of was
relied upon in the June 26, 2001, rulemaking. This modeling shows that
it is impossible to attain the NAAQS in St. Louis in 2002. The
significant factor is long-range transport. This suggests that
variations in out-of-state transport may account for the monitored
improvements in air quality.
Response 21: Previous modeling referred to by the commenter was
conducted as part of the attainment demonstration approved by EPA in
the June 26, 2001, rulemaking (66 FR 33995). (This approval was vacated
by the U.S. Court of Appeals for the Seventh Circuit, as explained
previously.) This modeling demonstrated that utilizing planned controls
and measures the area will attain the standard by no later than
November 15, 2004. EPA disagrees with the commenter's assertion that
the modeling demonstrated it was impossible to attain the standard in
2002. The purpose of the modeling was to determine the likelihood of
attainment. EPA's approval of the states' attainment demonstrations did
not include a determination that attainment or maintenance of the
standard prior to 2004 was impossible.
The assumptions used in the modeling for the attainment
demonstration approved in the June 26, 2001, rulemaking are described
in an April 3, 2001, proposal (66 FR 17649-17652). In this discussion,
EPA noted that the states incorporated corrections to the 1996 base
year emissions inventory, an assessment of the model's performance by
applying statistical tests, and assumptions regarding which states are
affected by the NO_X SIP call including NO_X limits
on facilities.
As discussed in the April 2001 document, the states had taken
measures to revise the emissions inventory to reflect the most current
data inputs available. In addition, an evaluation of the model was
performed as a measure of the ``likelihood'' that the standard will be
achieved. The June 26, 2001, rulemaking at 66 FR 17652 states:

The states conclude, and EPA concurs, that the revised modeling
system performs at an acceptable level because it satisfactorily
reproduces peak ozone concentrations relative to the monitored peak
ozone concentrations. The modeling system adequately simulates the
observed magnitude and spatial and temporal patterns of monitored
ozone concentrations. Furthermore, the modeling results accurately
differentiate between days with marginal ozone levels and days with
elevated ozone concentrations. Therefore, based on the revised
modeling and WOE results presented by the states which confirm the
adequacy of the adopted emission control strategy, EPA is approving
the states' attainment demonstrations.

The conclusions made regarding the likelihood of attainment based
upon the attainment demonstration modeling were the best that could be
drawn from the available information. And, it is likely that different
conclusions regarding attainment would be drawn if the states were
required to conduct modeling as part of the maintenance demonstration.
For example, if a prospective maintenance demonstration were performed
with an ozone photochemical model following EPA guidance, the modeling
would be allowed to use episode days from the 2000-2002 period, not
1991 and 1995 as was used in the attainment demonstration modeling. In
addition, the modeling would use a more current base-year inventory
(1999 or 2000) rather than the 1996 base-year inventory used in the
attainment demonstration modeling. It is highly likely, if not certain,
that the outcome would be a conclusion that attainment will be
preserved through the required 10-year period.
Ozone models are designed to primarily predict the relative impacts
of emission changes on future ozone levels. Thus, it is not uncommon to
observe that actual monitored ozone concentrations are different from

[[Page 25434]]

modeled values at certain locations. The commenter's assertion that
attaining the standard in 2002 is impossible is not supported by the
existing science.
The commenter does not provide data to support its hypothesis that
variations in out-of-state transport may account for the improvement in
air quality. The commenter only speculates that out-of-state transport
may account for the improvement in air quality. As described in the
response to comments 19 and 20 above, the states demonstrated that
improvements in air quality are due to permanent and enforceable
emission controls which have resulted in emission reductions, an
analysis of meteorological conditions which has shown no significant
decrease in the annual number of days conducive to ozone formation,
while there has been a significant reduction in monitored ozone
concentrations, and an assessment of emissions in 1990 and 2000 which
has shown decreased emissions of VOCs and NO_X. Thus, the
states have demonstrated the improvements in the St. Louis area are due
to permanent enforceable reductions in the St. Louis area.

E. Comments Related to Criterion 4: The Area Must Have a Fully Approved
Maintenance Plan Meeting the Requirements of Section 175A

Comment 22: Section 175A(a) of the CAA requires that state
maintenance plans must be SIP revisions. Section 110(a)(2)(A) of the
CAA requires a SIP to contain enforceable emission limitations. The
maintenance plans for each state do not include any enforceable
emission limitations. For example, Missouri NO_X controls
have not yet been promulgated.
Response 22: This comment refers to both the Missouri and Illinois
portions of the St. Louis area. EPA is hereby providing a response
regarding the Missouri portion of the St. Louis area. See the
rulemaking in today's Federal Register regarding redesignation of the
Illinois portion of the St. Louis area for EPA's response to this
comment as it pertains to the Illinois portion of the St. Louis area.
In this rulemaking, EPA is approving Missouri's maintenance plan as
a SIP revision.
The CAA requires the area to have a fully approved SIP and to have
met all of the applicable requirements of the CAA. The area's SIP
satisfies these requirements as described in this final rule and in
EPA's proposed rulemaking published on January 30, 2003 (68 FR 4847).
The measures that the states are relying on to maintain the 1-hour
ozone standard have been approved into the SIPs and are state and
Federally enforceable. This includes Missouri's NO_X RACT
rule found at 10 CSR 10-5.510 and the statewide NO_X rule
found at 10 CSR 10-6.350. (See response to comment 10 above regarding
the NO_X SIP Call.) The states must continue to implement
these measures as provided for in the Federally-approved SIPs.
The CAA does not require a separate level of enforcement for a
maintenance plan as a prerequisite to redesignation. The enforcement
program approved for and applicable to the SIPs as a whole also applies
to the maintenance plan. See discussion in the Cincinnati redesignation
(65 FR 37879, 37881-37882), and the Sixth Circuit decision in Wall v.
EPA, 265 F. 3d at 438, upholding EPA's interpretation of the
requirement. As explained below in the response to comment 26, Missouri
has committed to continue to implement the measures included in the
approved SIP and relied on for maintenance of the standard.
All of the control measures which the states relied upon are SIP-
approved measures. EPA cannot withhold its approval of the maintenance
plan submitted by the states because of concerns that the states may,
at some future time, either submit a SIP revision to amend or remove a
program, or that the states may fail to implement these programs in the
St. Louis area. The Federally-approved SIP requirements remain in place
and enforceable until such time as EPA takes action to approve SIP
revisions to amend or remove them. This can only be done via Federal
rulemaking, which includes procedures for public comment and review.
Comment 23: Section 182(j), 40 CFR 51.112(b), the Calcagni memo,
and the General Preamble require the use of photochemical modeling to
demonstrate maintenance. EPA is overruling Congress, EPA regulations
and common sense by proposing to predict maintenance for ten years
without any modeling. Monitoring is more accurate to show past
concentrations, but modeling is required to predict future
concentrations. The commenter cites Ober v. U.S.E.P.A., 84 F.3d 304
(9th Cir. 1996) in support of its assertion.
Response 23: EPA disagrees with the commenter's assertion that the
use of photochemical modeling to demonstrate maintenance is required by
the CAA, EPA policy or EPA regulations. The EPA is not overruling
Congress, or EPA regulations.
Section 175A requires states to develop and submit, as a SIP
revision, a plan for maintaining the NAAQS for at least 10 years after
redesignation. The plan shall contain such additional measures, if any,
as the Administrator deems necessary to ensure such maintenance.
Section 175A does not require modeling.
Section 182(j) contains no reference to maintenance plans. Section
182(j)(1) requires that each state in a multi-state ozone nonattainment
area shall ``* * * (A) take all reasonable steps to coordinate,
substantively and procedurally, the revisions and implementation of
State implementation plans applicable to the nonattainment area
concerned; and (B) use photochemical grid modeling or any other
analytical method determined by the Administrator, in his discretion,
to be at least as effective.'' The language in this section clearly
refers to ``nonattainment'' areas. Thus, EPA believes that Section
182(j) is applicable to attainment demonstrations, not maintenance plans.
Even if the commenter is correct in its assertion that section
182(j) applies to maintenance plans, this section does not necessarily
require modeling. EPA has the discretion to use other analytical
methods determined to be at least as effective. In the Calcagni memo on
page 9 EPA stated ``A State may generally demonstrate maintenance of
the NAAQS by either showing that future emissions of a pollutant or its
precursors will not exceed the level of the attainment inventory, or by
modeling to show that the future mix of sources and emission rates will
not cause a violation of the NAAQS.'' By this policy, EPA has, in
effect, expressed how its discretion will be utilized regarding the use
of emissions in lieu of modeling in demonstrating maintenance. In
addition, the Sixth Circuit in Wall v. EPA (265 F.3d 426, 435)
determined that ``EPA's actions are completely consistent with its own
interpretive memorandum, which allows for NAAQS maintenance to be
demonstrated by showing that the future emissions of a pollutant's
precursors will not exceed the level that allowed the area to achieve
attainment in the first place.'' See also EPA's discussion in its brief
in the Wall case. The Ober case cited by the commenter deals with
modeling requirements for approval of a SIP revision in a nonattainment
area for particulate matter, and has no relevance to the ozone
maintenance plan at issue here.
The regulation at 40 CFR 51.112(a) requires the SIP to demonstrate
that the measures, rules and regulations contained in the plan are
adequate to provide for the timely attainment and maintenance of the
NAAQS. The regulation at 40 CFR 51.112(b) specify

[[Page 25435]]

what the demonstration required in 40 CFR 51.112(a) must include. The
Sixth Circuit in Wall v. EPA (265 F.3d 426, 435) determined that EPA's
position that the regulation at 40 CFR 51.112(a) applies only to
attainment demonstrations and not maintenance plans is ``neither
impermissible nor in conflict with a statutory mandate * * *. Moreover,
EPA's actions are completely consistent with its own interpretive
memorandum, which allows for NAAQS maintenance to be demonstrated by
showing that the future emissions of a pollutant's precursors will not
exceed the level that allowed the area to achieve attainment in the
first place.''
Lastly, the proposed rule at 68 FR 4858 states that projected
emissions of NO_X in Illinois will be reduced from 141.64 to
96.67 tons per ozone season weekday from 2000 to 2014 and in Missouri,
they will be reduced from 453.14 to 317.58 tons per ozone season
weekday from 2000 to 2014. Projected emissions of VOCs in Illinois will
be reduced from 94.11 to 75.98 tons per ozone season weekday from 2000
to 2014 and in Missouri, they will be reduced from 248.35 to 182.57
tons per ozone season weekday from 2000 to 2014. A ``common sense''
conclusion is that further emission reductions are projected to occur
through 2014. Based on past trends of emissions decreases, reduced peak
ozone levels will continue from 2000 to 2014. Further modeling would
continue to demonstrate attainment. The commenter has not provided any
data to indicate that these reductions in ozone precursors would lead
to modeled increases in ozone concentrations.
Comment 24: EPA and the states have stated in testimony provided to
courts and the public that maintenance of the NAAQS in 2003 is not
possible. EPA and the states have stated that, due to upwind emissions,
attainment of the NAAQS cannot be achieved until 2004. EPA's modeling
demonstrates that it is not possible to assure that the NAAQS would be
maintained in 2003.
Response 24: The Commenter uses the same arguments in this comment
to state that the attainment of the NAAQS cannot be maintained as were
used in comment 21 above to claim that the area cannot attain the
NAAQS. See the response to comment 21 for further discussion.
EPA disagrees with the commenter's assertion that the modeling
demonstrated it was impossible to maintain the standard in 2003. The
purpose of the modeling is to predict the likelihood of attainment.
EPA's approval of the states' attainment demonstrations did not include
a determination that attainment or maintenance of the standard prior to
2004 was impossible.
The commenter refers to documents submitted by EPA and the states,
as well as to language used in various rulemakings stating, in effect,
that reductions in upwind emissions are necessary for attainment of the
standard and that the earliest attainment date is projected to be
November 15, 2004. At the time these documents were developed, EPA and
the states were basing their conclusions on the attainment
demonstration and the accompanying modeling. The statements made were
the best conclusions that could be drawn from the available information.
The conclusion that the maintenance plan will provide for
maintenance of the NAAQS for the next ten years as required by section
175A is based, in part, on more recent information than what was relied
upon in the attainment demonstration which included the modeling
referred to by the commenter. The maintenance plan includes an emission
inventory which is more recent than the inventory used in the
attainment demonstration. See the response to comment 36 for further
discussion.
EPA has no data to support the commenter's hypothesis that
variations in out-of-state transport may account for the improvement in
air quality. The commenter only speculates that out-of-state transport
solely account for the improvement in air quality. EPA concludes that
the plan demonstrates maintenance through 2014.
Comment 25: The SIP must provide assurance that the states have
adequate personnel, funding and authority to carry out the SIP. The
record for this action must provide real evidence of this assurance.
Response 25: This comment refers to both the Missouri and Illinois
portions of the St. Louis area. EPA is hereby providing a response
regarding the Missouri portion of the St. Louis area. See the
rulemaking in today's Federal Register regarding redesignation of the
Illinois portion of the St. Louis area for EPA's response to this
comment as it pertains to the Illinois portion of the St. Louis area.
EPA disagrees with the commenter that this action must include in
the record further evidence of resource commitments. The analysis has
already been performed in prior rulemakings and need not be reopened
here. See the redesignation of Cincinnati (65 FR 37881-37882),
Pittsburgh (66 FR 53102), and Cleveland (65 FR 77308, 77315) for
additional examples in which EPA has taken this position. See also,
Southwestern Pennsylvania Growth Alliance v. Browner, 144 F.3d 984 (6th
Cir. 1998).
In a final rulemaking action published on April 9, 1980 (45 FR
24146), EPA approve Missouri's SIP as meeting the financial and
manpower resource commitments of the CAA.
The Sixth Circuit in Wall v. EPA (265 F.3d 426, 437) determined
regarding resource and authority commitments for enforcement that
``there is no language in the CAA or in the EPA's regulations that
specifically requires that a separate commitment be made within the
maintenance plans themselves * * *. Morever, this decision is in accord
with the interpretation given to the CAA under the Calcagni Memorandum,
advising that `an EPA action on a redesignation request does not mean
that earlier issues with regard to the SIP will be reopened,' an
interpretation that has been upheld by this court.''
EPA also notes that more recent resource commitment reviews have
been performed. For example, in the February 17, 2000, proposed rule at
65 FR 8099 EPA noted that in proposing to approve Missouri's I/M
program, the ``the SIP includes a detailed budget plan that describes
the source of funds for personnel, program administration, program
enforcement, and purchase of equipment. * * * The SIP meets the Federal
requirements for evidence of adequate tools and resources under 40
CFR.51.372 and 51.354.''
Comment 26: EPA policy states that a state may not relax existing
controls upon redesignation. However, the states are moving LAER,
offsets and NO_X RACT to the contingency plan without a
modeling demonstration showing that these control measures are not
needed for attainment, contrary to EPA policy.
Response 26: This comment refers to both the Missouri and Illinois
portions of the St. Louis area. EPA is hereby providing a response
regarding the Missouri portion of the St. Louis area. See the
rulemaking in today's Federal Register regarding redesignation of the
Illinois portion of the St. Louis area for EPA's response to this
comment as it pertains to the Illinois portion of the St. Louis area.
Missouri has a commitment on page 29 of the maintenance plan which
states ``The department provides assurance that all of the control
measures adopted by state rules and listed in the ROP plan or this
document will be enforced to ensure maintenance of the one-hour ozone
NAAQS.''
The commenter refers to the Calcagni memo at page 10 which states
that ``the

[[Page 25436]]

State will be expected to maintain its implemented control strategy
despite redesignation to attainment, unless such measures are shown to
be unnecessary for maintenance or are replaced with measures that
achieve equivalent reductions.''
Section 175A requires that maintenance plans shall contain
contingency provisions deemed necessary to assure that the states will
promptly correct any violation of the standard which occurs after
redesignation of the area as an attainment area. These provisions shall
include a requirement that the state will implement ``all measures with
respect to the control of the air pollutant concerned which were
contained in the SIP for the area before redesignation of the area as
an attainment area.'' On page 6 of an October 14, 1994, memorandum
entitled, ``Part D New Source Review (part D NSR) Requirements for
Areas Requesting Redesignation to Attainment'' from Mary D. Nichols,
assistant Administrator for Air and Radiation, EPA stated its
interpretation on the term ``measures'' used in section 175A does not
include part D NSR permitting programs. In accordance with this
interpretation, EPA believes that lowest achievable emission rate
(LAER) and offsets, which are components of Missouri's part D NSR
permitting program, are not required to be retained following
redesignation of the St. Louis area as an attainment area.
LAER and offsets are specified in part D and subpart 2 of the CAA
applicable to nonattainment areas. Upon redesignation to attainment,
these requirements are no longer applicable. Removing the LAER and
offsets provision in the states' permitting programs is not contrary to
the above-mentioned policy. Upon redesignation to attainment, the LAER
requirements included in stationary source permits and the offsets
which were obtained by stationary sources at the time when the LAER and
offset provisions were in effect, will remain in effect for those
facilities. Thus, the LAER and offset measures which were relied upon
to attain the NAAQS will remain in effect following redesignation.
Following redesignation, any new facilities subject to the state's
permitting requirements will be subject, as a minimum, to the
Prevention of Significant Deterioration (PSD) requirements of Part C of
Title I of the CAA. (In Missouri, the LAER and offset requirements
remain in effect, unless the NSR rules are revised by the state and the
revision is approved by EPA.) Under the PSD requirements, the states
must ensure that such new facility will not cause a significant
deterioration of air quality to the extent that it causes or
contributes air pollution in excess of the NAAQS (Section 165). As part
of the PSD program sources are required to perform a source-specific
air quality demonstration to show no adverse impact on the NAAQS. Thus,
maintenance of the NAAQS is an inherent feature of the PSD program,
should Missouri choose not to retain its current program for new source
permitting in the future.
As for NO_X RACT, Missouri has an approved NO_X
RACT rule which will remain in effect following redesignation. Thus,
there will be no relaxation of NO_X RACT in Missouri
following redesignation.
Regarding modeling, the Shapiro Memo at page 6 states that ``States
may be able to move SIP measures to the contingency plan upon
redesignation if the State can adequately demonstrate that such action
will not interfere with maintenance of the standard.'' As stated above,
for Missouri, all control measures established prior to redesignation
as a result of the LAER and offset requirements are being retained
following redesignation and NO_X RACT is being retained.
Comment 27: The contingency provision of the maintenance plan fall
short of those required. All serious area requirements of Section
182(c) of the CAA must be included in the contingency plan and
implemented promptly in case of a violation. Virtually none of these
provisions are included in the contingency plan and thus cannot be
approved.
Response 27: EPA disagrees with the commenter's assertion that all
the serious area requirements of section 182(c) are required to be
included in the contingency plan and implemented in case of a violation.
The requirements for maintenance plans and contingency measures are
set forth in section 175A(d). Section 175A(d) states:

Each plan revision submitted under this section shall contain
such contingency provisions as the Administrator EPA deems necessary
to assure that the State will promptly correct any violation of the
standard which occurs after the redesignation of the area as an
attainment area. Such provisions shall include a requirement that
the State will implement all measures with respect to the control of
the air pollutant concerned which were contained in the State
implementation plan for the area before redesignation of the area as
an attainment area.

None of the serious area requirements was an applicable requirement
that was contained in the SIP prior to redesignation. The plan must
contain contingency measures that the Administrator deems appropriate
to assure that the states ``will promptly correct any violation of the
standard which occurs after the redesignation of the area as an
attainment area.'' As described in response to comment 28 below, EPA
believes that this requirement has been met. The statute does not
require that all serious area requirements be included in the
maintenance plan as contingency measures but rather that all measures
included in the SIP prior to redesignation be included in the
maintenance plan as contingency measures. As explained previously,
certain serious area requirements need not be met in the case of St.
Louis since they are not yet due. Since these provisions are not
applicable in St. Louis, they do not need to be included in the
maintenance plan as contingency measures.
The commenter's assertion that ``there is no implementation plan
applicable to this `serious area' '' is addressed in other responses in
this rulemaking. See, e.g., response to comment 17.
Comment 28: 42 U.S.C. 7505a(d) requires that the states will
promptly correct any violation of the standard which occurs after
redesignation. However, there is nothing in either contingency plan
which assures prompt correction of future violations. The plans contain
no adopted measures, and no schedule to adopt specific measures. The
plans offer to adopt an unspecified measure within eighteen months of
notification of a violation. This is an unreasonably long period. The
plans should require adoption in much less than eighteen months and
immediate implementation.
Response 28: This comment refers to both the Missouri and Illinois
portions of the St. Louis area. EPA is hereby providing a response
regarding the Missouri portion of the St. Louis area. See the
rulemaking in today's Federal Register regarding redesignation of the
Illinois portion of the St. Louis area for EPA's response to this
comment as it pertains to the Illinois portion of the St. Louis area.
EPA disagrees that Missouri's maintenance plan lacks adequate
contingency provisions should the area violate the standard. As stated
in the January 30, 2003, proposed rule at 68 FR 4859, the contingency
plan portion of the maintenance plans delineated Missouri's planned
actions in the event of future 1-hour ozone standard violations,
increasing ozone levels threatening a subsequent violation of the ozone
standard, and unanticipated

[[Page 25437]]

increases in ozone precursor emissions threatening a subsequent
violation of the ozone standard. Missouri has developed a contingency
plan with several levels of triggered actions depending on whether the
ozone standard has actually been violated after the redesignation of
the area to attainment or whether a subsequent violation of the ozone
standard is threatened on the basis of increased ozone concentrations
approaching the standard or unanticipated significant increases in
ozone precursor emissions. Missouri has also committed to continue to
implement all control measures included in the SIP prior to
redesignation consistent with section 175A(d) of the CAA.
The action trigger levels and planned corrective actions in the
contingency plan are the following:
A Level I Trigger will be exceeded if: (1) The monitored ambient
ozone levels exceed 124 parts per billion, one-hour averaged, more than
once per year at any monitoring site in the St. Louis maintenance area
(the current St. Louis ozone nonattainment area), or more than two
exceedances in any two- or three-year period; or (2) the St. Louis
maintenance area's VOC or NO_X emissions for 2005 or 2008
increase more than 5 percent above the 2000 attainment levels. In the
event one of these action trigger levels are exceeded, Illinois and
Missouri will work together to evaluate the situation and determine if
adverse emissions trends are likely to continue. If so, the states will
determine what and where emission controls may be required to avoid a
violation of the 1-hour ozone NAAQS. A study shall be completed within
nine months of the determination of the action trigger exceedance.
A Level II Trigger will be exceeded if a violation of the 1-hour
ozone NAAQS at any monitoring site in the St. Louis ozone maintenance
area is recorded after the area is redesignated to attainment of the
standard. If this trigger is exceeded, Illinois and Missouri will work
together to conduct a thorough analysis to determine appropriate
measures, from those listed below, to address the cause of the ozone
standard violation.
The contingency plan for Missouri lists a number of possible
contingency measures. The plan calls for the appropriate contingency
measures to be adopted and implemented within 18 months of a Level I or
Level II trigger being exceeded. The list of possible contingency
measures in Missouri's contingency plan include the following:
Point Source Measures
? NO_X SIP Call Phase II (non-utility)
? Apply RACT to smaller existing sources
? Tighten RACT for existing sources covered by EPA Control
Techniques Guidelines
? Expanded geographic coverage of current point source measures
? MACT for industrial sources
? New source offsets and Lowest Achievable Emission Rates
? Other measures to be identified
Mobile Source Measures
? Transportation Control Measures, including, but not limited
to, area-wide rideshare programs, telecommuting, transit improvements,
and traffic flow improvements.
? High Enhanced I/M (OBDII)
? California Engine Standards
? Other measures to be identified
Area Source Measures
? California Architectural/Industrial Maintenance (AIM)
? California Commercial and Consumer Products
? Broader geographic applicability of existing measures
? California Off-road Engine Standards
? Other measures to be identified
As stated in the September 4, 1992, Calcagni memo, page 12, ``For
purposes of section 175A, a State is not required to have fully adopted
contingency measures that will take effect without further action by
the State in order for the maintenance plan to be approved. However,
the contingency plan is considered to be an enforceable part of the SIP
and should ensure that the contingency measures are adopted expediently
once they are triggered.'' Thus, EPA has long interpreted section 175A
not to require that contingency measures have already been adopted.
On July 21, 1983 (48 FR 33265), EPA approved Missouri rule 10 CSR
10-1.010, General Organization which set forth the organization, powers
and duties of the Missouri Air Conservation Commission. The rule
contained a new section (3) which described procedures to be followed
by the Air Pollution Control Program for providing public notice and
public participation in the rulemaking process.
In order to comply with 10 CSR 10-1.010, and the underlying statute
by which Missouri is authorized by the legislature to adopt
regulations, Missouri requires time to evaluate potential controls and
provide public notice and public participation in the rulemaking
process when adopting contingency measures. In addition, selected
controls would require a period of time for sources to install the
controls (e.g., RACT on smaller sources) or for an implementing agency
to fund and establish the new program (e.g., transportation control
measures). The commenter provided no rationale for its assertion that
an outside date of 18 months for adoption of measures is unreasonable.
The statute affords EPA discretion to determine whether the timeframe
for implementation of contingency measures is reasonable. EPA finds
that 18 months as described in the maintenance plan to adopt and
implement contingency measures is a reasonable time period for Missouri
to meet its regulatory obligations while meeting the requirement under
section 175A to promptly correct any violation of the standard. In
addition, this 18-month period to adopt and implement contingency
measures is consistent with other redesignations such as Pittsburgh (66
FR 53102) in which a 12- to 24-month time period was specified to adopt
and implement contingency measures. See also the Louisville
redesignation (66 FR 53665, October 23, 2001) approving an 18-month
schedule for implementation of contingency measures, and Northern
Kentucky (Cincinnati-Hamilton) (65 FR 37879, June 19, 2000) and (67 FR
49600, July 31, 2002).
Comment 29: Neither maintenance plan provides any procedure for
quantifying the reductions needed to correct violations.
Response 29: This comment refers to both the Missouri and Illinois
portions of the St. Louis area. EPA is hereby providing a response
regarding the Missouri portion of the St. Louis area. See the
rulemaking in today's Federal Register regarding redesignation of the
Illinois portion of the St. Louis area for EPA's response to this
comment as it pertains to the Illinois portion of the St. Louis area.
As indicated in the response to comment 28 above, the maintenance
plan refers to a violation of the NAAQS as a level II trigger. In the
event of a violation, Illinois and Missouri have committed to work
together to conduct a thorough analysis to determine appropriate
measures to address the cause of the ozone standard violation. It is
impossible for a state to determine, before a violation, what
reductions are necessary to correct a violation. For example, if
Missouri would select tightening RACT for existing sources as a
contingency measure, the amount of reductions by implementing this
measure is dependent upon the number of sources subject to RACT rules
in the

[[Page 25438]]

area at the time of the violation. Since the state has no control over
when a source ceases operating, it is impossible to determine, at this
time, how many sources will be affected by a tightening of RACT which
may be implemented at some unspecified time in the future. Thus it is
impossible to determine beforehand how much of a reduction will be
achieved by implementing this measure. See the discussion in the
Cuyohoga and Jefferson Counties, Ohio, redesignation for particulate
matter (65 FR 77308, December 11, 2000).
The approach taken in the maintenance plan is to conduct a thorough
analysis to determine the magnitude of the reductions needed to correct
the violation, the types of sources from which reductions must be made
(e.g., point, area, or mobile sources), and the mechanisms for
achieving the reductions. The list of contingency measures includes a
reasonable mix of measures from which to select the measures most
suited to address a future violation (a level II trigger), if one
occurs, or to alleviate an unanticipated decline in air quality (a
level I trigger). EPA finds that this is a reasonable approach which
will assure prompt correction of the violation. In addition, consistent
with the Calcagni memo, the maintenance plan includes a Level I trigger
in which Missouri will evaluate and determine if adverse emissions
trends are likely to continue. If so, Missouri will determine what and
where emission controls may be required to avoid a violation of the 1-
hour ozone NAAQS.
Comment 30: The contingency measures in the maintenance plans are
vague and open ended. Neither plan identifies any measures to be
adopted. No firm schedule for adoption and implementation is included.
Response 30: This comment refers to both the Missouri and Illinois
portions of the St. Louis area. EPA is hereby providing a response
regarding the Missouri portion of the St. Louis area. See the
rulemaking in today's Federal Register regarding redesignation of the
Illinois portion of the St. Louis area for EPA's response to this
comment as it pertains to the Illinois portion of the St. Louis area.
EPA disagrees with the commenter's assertion that the contingency
measures are vague and open ended. In response to comments 28 and 29
above, EPA addressed the procedures contained in the maintenance plan
for evaluating which measures are necessary to promptly correct a
violation.
In addition, in response to comment 28 above, EPA identified the
list of potential contingency measures contained in Missouri's
maintenance plan along with a schedule of 18 months to adopt and
implement selected contingency measures in the event of a violation (a
level II trigger) or a decline in air quality (a level I trigger). EPA
has concluded that the maintenance plan satisfies statutory
requirements and EPA guidance regarding adoption and implementation of
contingency measures consistent with EPA guidance and the CAA. The
commenter acknowledges this 18-month time period to adopt and implement
contingency measures in the comments.
Comment 31: Each maintenance plan contains inadequate provisions to
respond to anticipated violations of the NAAQS. Anticipated violations
are based upon inventories exceeding the 2000 inventory or two
exceedances at any monitoring site. There is no commitment to adopt any
additional controls to address anticipated violations.
Response 31: This comment refers to both the Missouri and Illinois
portions of the St. Louis area. EPA is hereby providing a response
regarding the Missouri portion of the St. Louis area. See the
rulemaking in today's Federal Register regarding redesignation of the
Illinois portion of the St. Louis area for EPA's response to this
comment as it pertains to the Illinois portion of the St. Louis area.
As indicated above, a Level I Trigger will be exceeded if: (1) The
monitored ambient ozone levels exceed 124 parts per billion, one-hour
average, more than once per year at any monitoring site in the St.
Louis maintenance area (the current St. Louis ozone nonattainment
area), or more than two exceedances in any two-or three-year period; or
(2) the St. Louis maintenance area's VOC or NO_X emissions
for 2005 or 2008 increase more than 5 percent above the 2000 attainment
levels. In the event one of these action trigger levels is exceeded,
Illinois and Missouri will work together to evaluate the situation and
determine if adverse emissions trends are likely to continue. If so,
the states will determine what and where emission controls may be
required to avoid a violation of the 1-hour ozone NAAQS. The emission
controls will be selected from a list of measures included in the
contingency plan. A study shall be completed within nine months of the
determination of the action trigger exceedance, and Missouri's
maintenance plan contains a commitment to adopt and implement the
necessary contingency measures within 18 months of a Level I trigger
consistent with the discretion afforded EPA by the statute. The
contingency plan meets the requirement of section 175A(d) and the
applicable guidance in the Calcagni memo.
Comment 32: The maintenance plans contain no commitment to
implement measures in the SIP. EPA cannot approve the maintenance plan
without this commitment.
Response 32: This comment refers to both the Missouri and Illinois
portions of the St. Louis area. EPA is hereby providing a response
regarding the Missouri portion of the St. Louis area. See the
rulemaking in today's Federal Register regarding redesignation of the
Illinois portion of the St. Louis area for EPA's response to this
comment as it pertains to the Illinois portion of the St. Louis area.
The commenter is incorrect in its statement that the maintenance
plan does not contain a commitment to implement measures in the SIP.
Such a commitment was included in Missouri's maintenance plan. Section
5.4 of Missouri's maintenance plan states the following: ``The
department provides assurance that all of the control measures adopted
by state rules and listed in the ROP plan or this document will be
enforced to ensure maintenance of the one-hour ozone NAAQS. Any
revisions to the control measures included as part of the maintenance
plan will be submitted as a SIP revision to EPA for approval.'' As
described in response to comment 28, Missouri is retaining all of the
measures contained in its SIP prior to redesignation.
Comment 33: The maintenance plans do not address expected growth in
areas adjacent to the nonattainment area such as Ste. Genevieve County.
An assessment of this growth should be included. Also, the plan is
based on the ``irrational assumption'' that ``if there is no increase
in emissions, and no decrease in controls, the standard will be
maintained.''
Response 33: This comment refers to both the Missouri and Illinois
portions of the St. Louis area. EPA is hereby providing a response
regarding the Missouri portion of the St. Louis area. See the
rulemaking in today's Federal Register regarding redesignation of the
Illinois portion of the St. Louis area for EPA's response to this
comment as it pertains to the Illinois portion of the St. Louis area.
The commenter's characterization of the ``basic premise'' of the
maintenance plan is incorrect. The plan does not simplistically assume
that there will be no increase in emissions. The plan carefully
projects the growth in emissions which will occur in various source
sectors, and the reductions which will occur based on emission

[[Page 25439]]

control programs which are in place, in order to determine the net
change in emissions from 2000-2014. The states are required to and have
applied the appropriate techniques to estimate and account for
potential emissions changes in the area. These techniques are
necessarily based on sector-based growth indicators (positive and
negative), i.e., sector-specific economic factors, because the states
have no way of predicting specific changes which take place within the
emissions inventory.
Specific projects, such as those cited by the commenter, are
addressed through mechanisms other than maintenance plans. Missouri
implements Prevention of Significant Deterioration and NSR permitting
regulations. These regulations address the air quality impacts of new
sources and modifications of existing sources both inside and outside
the boundaries of the nonattainment area. They are designed to prevent
new source construction or existing source expansion which would
adversely affect an area's ability to attain or maintain a national
standard. The anticipated plant referenced by the commenter is a
potential source in Missouri and the state is currently in the process
of reviewing construction permit applications under state permitting
requirements. This plant has not received the preconstruction permit
necessary for construction and operation. Before any such project can
be permitted, a permit applicant would be required, among other
requirements, to identify specific emission increases and decreases
associated with a particular project and demonstrate that the project
would not have a significant adverse impact on an ambient air quality
standard. Missouri regulation 10 CSR 10-6.060, Missouri's construction
permitting rule, is part of the Federally-approved SIP.
EPA believes that it is the function of the state's air permitting
rules, rather than the maintenance plan, to ensure that specific
potential new sources do not create emissions which would interfere
with the maintenance of the ozone standard.
Comment 34: The emission estimates are unreliable. A recent study
of flares throws doubt into the St. Louis emission inventory. EPA must
consider the significant underestimation of flare emissions in the
emission inventory.
Response 34: This comment refers to both the Missouri and Illinois
portions of the St. Louis area. EPA is hereby providing a response
regarding the Missouri portion of the St. Louis area. See the
rulemaking in today's Federal Register regarding redesignation of the
Illinois portion of the St. Louis area for EPA's response to this
comment as it pertains to the Illinois portion of the St. Louis area.
EPA believes that the states used the appropriate emission
estimates in developing the emission inventory. The commenter cites a
study of emissions from flares reported by the Bay Area Management
District which the commenter alleges shows that the states greatly
underestimated emissions from flares. EPA does not agree that the study
cited by the commenter renders the emission estimates unreliable.
The Bay Area Management Study referenced by the commenter is a
draft document and specifically states on the first page ``Do not cite
or quote.'' This document is currently undergoing scientific review.
Therefore, no conclusions or comparisons should be drawn from this
study until it becomes final. This study specifically addresses
refinery flare emissions. However, no refineries are located in the
Missouri side of the non-attainment area. Further review of the
document has shown that methane was included in the emission factor
that was used to derive emissions for this study. Methane is not an
ozone precursor, and the inclusion of this pollutant could
significantly alter the preliminary findings. The study targets the
control efficiencies of the flares and states that ``efficiency drops
approximately by the cube of the speed (wind)''. This would suggest
that on high wind event days the control efficiencies would be at their
lowest. However, in the St. Louis area, high ozone days have been
characterized by low wind conditions, which would produce minimal
impact on flare control efficiencies during the periods of concern.
Lastly, NO_X and VOC emissions from all flares constitute
less than one-tenth of one percent of the total inventory for the
Missouri side of the St. Louis area. Therefore, any potential changes
in calculation methodology from this source category, even if changes
were warranted based on this draft study, would still likely produce an
insignificant change to the total inventory.
Comment 35: Missouri states that it operates an enhanced I/M
program but this has never been authorized by the Missouri legislature.
Response 35: The Missouri Legislature authorized MDNR to develop an
I/M program, including a centralized test only program, as necessary to
provide for attainment and maintenance of the national ambient air
quality standard. That authority is codified in the Missouri Revised
Statutes, Sections 643.300--643.355. Missouri's I/M program has
incorporated most of the features of an enhanced program, described in
our 2000 rulemakings (65 FR 8097, February 17, 2000 and 65 FR 31480,
May 18, 2000).
The I/M program operated in the St. Louis, Missouri, area is known
as the Gateway Clean Air Program. The Gateway Clean Air Program
utilizes transient emission testing, the IM240 test, at centralized
testing stations. These features are commonly thought of as being
associated with an ``enhanced'' I/M program, as compared with
decentralized, idle test programs. The IM240 test measures the vehicle
under various operating conditions, measures NO_X, and makes
these measurements in terms of grams per mile, all of which the idle
test cannot. Additionally, the Gateway Clean Air Program includes gas
cap testing, which addresses evaporative hydrocarbon emissions that a
tailpipe test cannot. Thus, Missouri often refers to the Gateway Clean
Air Program as an Enhanced I/M program. As seen in Missouri's December
2002 program evaluation, this program is achieving emission reductions
beyond those which would be achieved through a decentralized, idle test
program. The descriptive terminology is irrelevant in any event.
Missouri has assumed emissions reductions for the program it has in
place (whatever label is used to describe the program), and the
commenter does not provide any information indicating that the assumed
reductions are not appropriate.
Comment 36: The emission inventory submitted by Missouri is not an
inventory of emissions during the attainment period but is projected
emissions drawn from Missouri's old attainment demonstration. EPA
cannot conclude that keeping emissions no higher than these projected
inventory amounts will ensure maintenance of the NAAQS.
Response 36: Missouri did not use the same inventories in the
attainment demonstration as was used in the maintenance plan. Missouri
used a 1995/1996 inventory for the attainment demonstration and a 1999
inventory for the maintenance plan.
In the maintenance plan, Missouri selected 2000 as ``the attainment
year'' for purposes of demonstrating attainment of the 1-hour ozone
NAAQS. Both point and area source inventories were grown from 1999
emission inventories. To demonstrate maintenance of the ozone standard
through a ten-year maintenance period, Missouri projected VOC and
NO_X emissions for the St. Louis area to 2007

[[Page 25440]]

and 2014 and compared these projected emissions to the 2000 attainment
year emissions. The 2007 emission estimates were generated to test a
midpoint in the ten-year maintenance period.
In the April 17, 2000, proposed rule at 65 FR 20411 for the
attainment demonstration, EPA noted that ``The state submittals
describe in detail the procedures used to develop, and then project,
the base year emission inventories to the 1995/1996 period and to
project emission to account for growth and control through 2003.'' The
maintenance plan does not rely on these inventories.
As stated in response to comment 23 above, keeping emissions no
higher than those projected in the inventory will ensure maintenance of
the NAAQS. The Sixth Circuit in Wall v. EPA (265 F.3d 426, 435)
determined that ``EPA's actions are completely consistent with its own
interpretive memorandum, which allows for NAAQS maintenance to be
demonstrated by showing that the future emissions of a pollutant's
precursors will not exceed the level that allowed the area to achieve
attainment in the first place.''
Comment 37: Neither maintenance plan provides a technical analysis
demonstrating that maintenance of the 2000 emission levels will assure
maintenance of the NAAQS. Such a demonstration requires photochemical
grid modeling.
Response 37: This comment refers to both the Missouri and Illinois
portions of the St. Louis area. EPA is hereby providing a response
regarding the Missouri portion of the St. Louis area. See the
rulemaking in today's Federal Register regarding redesignation of the
Illinois portion of the St. Louis area for EPA's response to this
comment as it pertains to the Illinois portion of the St. Louis area.
EPA disagrees that modeling is required to demonstrate maintenance
of the NAAQS. EPA reiterates its response to other comments including
comments 23 and 36 in that the Court of Appeals for the Sixth Circuit
in Wall v. EPA (265 F.3d 426, 435) determined that ``EPA's actions are
completely consistent with its own interpretive memorandum, which
allows for NAAQS maintenance to be demonstrated by showing that the
future emissions of a pollutant's precursors will not exceed the level
that allowed the area to achieve attainment in the first place.''
Missouri's maintenance plan includes a technical analysis as
described in the response to comment 28 above that demonstrates
maintenance of the NAAQS, based on a comparison of base year
(attainment year) and projected VOC and NO_X emissions. This
analysis meets the requirements of the CAA, is consistent with EPA
guidance, and demonstrates maintenance of the NAAQS.
Comment 38: The maintenance plan must include RACM and RACT, for
the reasons stated in comment 13 above.
Response 38: EPA incorporates its response to comment 13 in
response to this comment.

F. Comments Related to Criterion 5: The Area Must Have Met All
Applicable Requirements Under Section 110 and Part D

Comment 39: Neither state has met all the requirements applicable
to the area. The serious area requirements of section 182(c) are
applicable but none of these requirements have been met. Some of the
requirements are applicable and enforceable now, such as the 50 ton per
year threshold for permitting and enforcement and paragraphs 7, 8, and
10 of section 182(c).
Response 39: This comment refers to both the Missouri and Illinois
portions of the St. Louis area. EPA is hereby providing a response
regarding the Missouri portion of the St. Louis area. See the
rulemaking in today's Federal Register regarding redesignation of the
Illinois portion of the St. Louis area for EPA's response to this
comment as it pertains to the Illinois portion of the St. Louis area.
As stated in the response to comments 6 through 11 above, the SIPs
meet the applicable requirements and the serious area requirements are
not applicable for purposes of this redesignation. States requesting
redesignation to attainment must meet the relevant CAA requirements
that come due prior to the submittal of a complete redesignation
request. Areas may be redesignated even though they have not adopted
measures that come due after the submission of a complete redesignation
request. Upon completion of today's actions, the SIP is fully approved
for all applicable regulations. SIP revisions addressing the serious
area requirements were required to be submitted by January 30, 2004.
Section 182(c) paragraphs 7 and 8 refer to special rules for
modifications of major sources while paragraph 10 refers to 1.2 to 1
offset requirements for serious nonattainment areas. Missouri rule 10
CSR 10-6.020 defines the Missouri portion of the St. Louis area as a
moderate ozone nonattainment area. A SIP revision would be required to
redefine the Missouri portion of the St. Louis area to a serious
nonattainment area. As stated in response to comment 7, EPA established
a future date for submission of the serious area requirements,
including section 182(c)(7),(8), and (10), and the requirements are not
now applicable for purposes of this redesignation.

G. Comments Related to Implementation of Contingency Measures

Comment 40: One commenter requested that in the final rule, EPA
expressly state that in the event of a future violation of the NAAQS,
Illinois and Missouri will not necessarily be required to evaluate any
particular contingency measure nor be required to submit further
attainment demonstrations.
Response 40: As stated above, the contingency plan portion of each
state's maintenance plans delineate the states' planned actions in the
event of future 1-hour ozone standard violations, increasing ozone
levels threatening a subsequent violation of the ozone standard, and
unanticipated increases in ozone precursor emissions threatening a
subsequent violation of the ozone standard. In the event of a level I
trigger, Illinois and Missouri will work together to evaluate the
situation and determine if adverse emissions trends are likely to
continue. If so, the states will determine what and where emission
controls may be required to avoid a violation of the 1-hour ozone
NAAQS. A study shall be completed within nine months of the
determination of the action trigger exceedance. In the event of a Level
II trigger, Illinois and Missouri will work together to conduct a
thorough analysis to determine appropriate contingency measures. EPA
expects that through this process, the states will identify the
appropriate measures to implement to maintain the NAAQS. Redesignated
areas are not subject to an obligation to meet additional nonattainment
area requirements such as attainment demonstrations since they are no
longer designated nonattainment areas. Instead, they must implement the
contingency measures, which is what Congress provided for in the CAA.

H. Comments Related to Redesignation of a Portion of the St. Louis Area

Comment 41: One commenter requested that in the event the EPA is
unable to finalize Missouri's I/M program, as proposed in a separate
rulemaking on January 30, 2003, EPA should proceed with the
redesignation for the Illinois portion of the St. Louis area.
Response 41: In today's Federal Register, EPA is approving
Missouri's revised I/M rule. In addition, as explained above, EPA is
finalizing its actions on the Missouri and Illinois

[[Page 25441]]

redesignation requests in separate rulemakings.

I. Comments Related to Interstate Transport

Comment 42: EPA must ensure that the CAA requirements of Section
110(a)(2)(D) pertaining to interstate transport impacts are actively
and adequately met through the states' SIPs and through federal control
programs such as the NO_X SIP call.
Response 42: This comment refers to both the Missouri and Illinois
portions of the St. Louis area. EPA is hereby providing a response
regarding the Missouri portion of the St. Louis area. See the
rulemaking in today's Federal Register regarding redesignation of the
Illinois portion of the St. Louis area for EPA's response to this
comment as it pertains to the Illinois portion of the St. Louis area.
As stated above, EPA believes that submissions under the
NO_X SIP call should not be considered applicable
requirements for purposes of evaluating a redesignation request. The
NO_X SIP call requirements are not linked with a particular
nonattainment area's designation and classification. EPA believes that
the requirements linked with a particular nonattainment area's
designation and classification are the requirements that are the
relevant measures to evaluate in reviewing a redesignation request. The
NO_X SIP call submittal requirements continue to apply to a
state regardless of the designation of any one particular area in the
state.
Thus, we do not believe that the NO_X SIP call submission
should be construed to be an applicable requirement for purposes of
redesignation. The section 110 and part D requirements, which are
linked with a particular area's designation and classification, are the
relevant measures to evaluate in reviewing a redesignation request.
This policy is consistent with EPA's existing conformity and oxygenated
fuels requirements, as well as with section 184 ozone transport
requirements. See Reading, Pennsylvania, proposed and final rulemakings
(61 FR 53174-53176, October 10, 1996), (62 FR 24826, May 7, 1997);
Cleveland-Akron-Lorain, Ohio, final rulemaking (61 FR 20458, May 7,
1996); and Tampa, Florida, final rulemaking (60 FR 62748, December 7,
1995). See also the discussion on this issue in the Cincinnati
redesignation (65 FR 37890, June 19, 2000).
Missouri has adopted and EPA has approved into the SIP a state-wide
NO_X rule (10 CSR 10-6.350 Emissions Limitations and
Emissions Trading of Oxides of Nitrogen (65 FR 82285, December 28,
2000). This rule will remain as a SIP requirement following
redesignation of the area to attainment. EPA is also determining in a
separate rulemaking (proposed at 67 FR 8396) whether or not the eastern
part of Missouri is to be subject to the NO_X SIP call in
response to a court remand.
Comment 43: The expected NO_X emission control programs
and emission reductions for the St. Louis area should not be
jeopardized due to the absence of continued federal enforceability of
the SIPs.
Response 43: The SIPSs will remain Federally enforceable following
redesignation of the St. Louis area to attainment. In addition, all of
the NO_X emission controls measures which are currently in
place will remain as SIP requirements following redesignation to
attainment. These emission control measures include NO_X
RACT, and the state-wide NO_X rule in Missouri. Any revisions
to SIP requirements would have to meet the applicable provisions of the
CAA and be approved by EPA.
Comment 44: The redesignation of the St. Louis area to attainment
should not weaken the impetus to rapidly address NO_X
transport to downwind areas. These efforts are critical to addressing
the 8-hour and 1-hour ozone NAAQS in the St. Louis and downwind areas.
Response 44: The St. Louis redesignation to attainment will not
delay EPA's decision as to whether or not the eastern portion of
Missouri is to be included in the NO_X SIP call. EPA will
closely review any proposed changes to the NO_X emission
control programs which are currently in place in the St. Louis area to
ensure that the proposed changes will not adversely affect the
maintenance of the NAAQS.

VI. Statutory and Executive Order Reviews

Under Executive Order 12866 (58 FR 51735, October 4, 1993), this
action is not a ``significant regulatory action'' and therefore is not
subject to review by the Office of Management and Budget. For this
reason, this action is also not subject to Executive Order 13211,
``Actions Concerning Regulations That Significantly Affect Energy
Supply, Distribution, or Use'' (66 FR 28355, May 22, 2001). This action
merely approves state law as meeting Federal requirements and imposes
no additional requirements beyond those imposed by state law.
Accordingly, the Administrator certifies that this rule will not have a
significant economic impact on a substantial number of small entities
under the Regulatory Flexibility Act (5 U.S.C. 601 et seq.). Because
this rule approves pre-existing requirements under state law and does
not impose any additional enforceable duty beyond that required by
state law, it does not contain any unfunded mandate or significantly or
uniquely affect small governments, as described in the Unfunded
Mandates Reform Act of 1995 (Public Law 104-4).
This rule also does not have tribal implications because it will
not have a substantial direct effect on one or more Indian tribes, on
the relationship between the Federal Government and Indian tribes, or
on the distribution of power and responsibilities between the Federal
Government and Indian tribes, as specified by Executive Order 13175
(65 FR 67249, November 9, 2000). This action also does not have Federalism
implications because it does not have substantial direct effects on the
States, on the relationship between the national government and the
States, or on the distribution of power and responsibilities among the
various levels of government, as specified in Executive Order 13132
(64 FR 43255, August 10, 1999). This action merely approves a state rule
implementing a Federal standard, and does not alter the relationship or
the distribution of power and responsibilities established in the CAA.
This rule also is not subject to Executive Order 13045 ``Protection of
Children from Environmental Health Risks and Safety Risks''
(62 FR 19885, April 23, 1997), because it is not economically significant.
In reviewing SIP submissions, EPA's role is to approve state
choices, provided that they meet the criteria of the CAA. In this
context, in the absence of a prior existing requirement for the State
to use voluntary consensus standards (VCS), EPA has no authority to
disapprove a SIP submission for failure to use VCS. It would thus be
inconsistent with applicable law for EPA, when it reviews a SIP
submission, to use VCS in place of a SIP submission that otherwise
satisfies the provisions of the CAA. Thus, the requirements of section
12(d) of the National Technology Transfer and Advancement Act of 1995
(15 U.S.C. 272 note) do not apply. This rule does not impose an
information collection burden under the provisions of the Paperwork
Reduction Act of 1995 (44 U.S.C. 3501 et seq.).
The Congressional Review Act, 5 U.S.C. 801 et seq., as added by the
Small Business Regulatory Enforcement Fairness Act of 1996, generally
provides that before a rule may take effect, the agency promulgating
the rule must submit a rule report, which includes a copy of the rule,
to each House of the Congress and to the Comptroller General of the
United States. EPA will submit a

[[Page 25442]]

report containing this rule and other required information to the U.S.
Senate, the U.S. House of Representatives, and the Comptroller General
of the United States prior to publication of the rule in the Federal
Register. A major rule cannot take effect until 60 days after it is
published in the Federal Register. This action is not a ``major rule''
as defined by 5 U.S.C. 804(2).
Under section 307(b)(1) of the CAA, petitions for judicial review
of this action must be filed in the United States Court of Appeals for
the appropriate circuit by July 11, 2003. Filing a petition for
reconsideration by the Administrator of this final rule does not affect
the finality of this rule for the purposes of judicial review nor does
it extend the time within which a petition for judicial review may be
filed, and shall not postpone the effectiveness of such rule or action.
This action may not be challenged later in proceedings to enforce its
requirements. (See section 307(b)(2).)

List of Subjects

40 CFR Part 52

Environmental protection, Air pollution control, Incorporation by
reference, Intergovernmental relations, Nitrogen dioxide, Ozone,
Reporting and recordkeeping requirements, Volatile organic compounds.

40 CFR Part 81

Environmental protection, Air pollution control, National parks,
Ozone, Wilderness areas.

Dated: April 29, 2003.
William W. Rice,
Acting Regional Administrator, Region 7.

? Chapter I, title 40 of the Code of Federal Regulations is amended as
follows:

PART 52--[AMENDED]

? 1. The authority citation for part 52 continues to read as follows:

Authority: 42 U.S.C. 7401 et seq.

Subpart AA--Missouri

? 2. In Sec. 52.1320(e) the table is amended by adding an entry at the
end of the table to read as follows:

Sec. 52.1320 Identification of Plan.

* * * * *
(e) * * *

EPA Approved Missouri Nonregulatory SIP Provisions
----------------------------------------------------------------------------------------------------------------
State EPA
Name of nonregulatory SIP provision Applicable geographic or submittal approval Explanation
nonattainment area date date
----------------------------------------------------------------------------------------------------------------

* * * * * * *
Maintenance Plan for the Missouri Portion St. Louis.................... 12/06/02 5/12/03
of the St. Louis Ozone Nonattainment Area
including 2014 On-Road Motor Vehicle
Emission Budgets.
----------------------------------------------------------------------------------------------------------------

PART 81--[AMENDED]

? 1. The authority citation for part 81 continues to read as follows:

Authority: 42 U.S.C. 7401 et seq.

? 2. In Sec. 81.326 the table entitled ``Missouri--Ozone (1-Hour
Standard)'' is amended by revising the entry for St. Louis Area to read
as follows:

Sec. 81.326 Missouri.

* * * * *

Missouri--Ozone
[1-Hour Standard]
----------------------------------------------------------------------------------------------------------------
Designation Classification
Designated area ---------------------------------------------------------------------------
Date \1\ Type Date \1\ Type
----------------------------------------------------------------------------------------------------------------

* * * * * * *
St. Louis Area:
Franklin County................. 5/12/03 Attainment.............
Jefferson County................ 5/12/03 Attainment.............
St. Charles County.............. 5/12/03 Attainment.............
St. Louis....................... 5/12/03 Attainment.............
St. Louis County................ 5/12/03 Attainment ............
----------------------------------------------------------------------------------------------------------------
\1\ This date is October 18, 2000, unless otherwise noted.

* * * * *
[FR Doc. 03-11187 Filed 5-9-03; 8:45 am]
BILLING CODE 6560-50-P

Notices For
2009
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Determination of Attainment of Ozone Standard, St. Louis Area; Approval and Promulgation of Implementation Plans, and Redesignation of Areas for Air Quality Planning Purposes, State of Missouri

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