1. ILLINOIS POLLUTION CONTROL BOARD
    2. SUBCHAPTER c: EMISSION STANDARDS AND LIMITATIONS FOR STATIONARY SOURCES PART 217 NITROGEN OXIDES EMISSIONS
    3. SUBPART A: GENERAL PROVISIONS
    4. SUBPART B: NEW FUEL COMBUSTION EMISSION SOURCES
      1. E = (AG + BL + CS) Q
    5. English
    6. Metric
    7. SUBPART C: EXISTING FUEL COMBUSTION EMISSION UNITS SOURCES
      1. E = (AG + BL + CS) Q
    8. English
    9. Metric
    10. UNact ≤ Nall
    11. UWhere:
    12. U1)U UActual emissions must be determined as follows:
    13. UWhen emission limits are prescribed in lb/mmBtu,
    14. UEMact(i) = Eact(i) x Hi/2000
    15. When emission limits are prescribed in lb/ton of processed product,
    16. EMact(i) = Eact(i) x Pi/2000
    17. 2) Allowable emissions must be determined as follows:
    18. When emission limits are prescribed in lb/mmBtu,
    19. EMall(i) = Eall(i) x Hi/2000
    20. When emission limits are prescribed in lb/ton of processed product,
    21. EMall(i) = Eall(i) x Pi/2000
    22. Where:

 
ILLINOIS POLLUTION CONTROL BOARD
July 23, 2009
IN THE MATTER OF:
NITROGEN OXIDES EMISSIONS FROM
VARIOUS SOURCE CATEGORIES:
AMENDMENTS TO 35 ILL. ADM. CODE
PARTS 211 AND 217
)
)
)
)
)
)
R08-19
(Rulemaking - Air)
Proposed Rule. Second Notice.
OPINION AND ORDER OF THE BOARD (by A.S. Moore):
Today the Board adopts for second notice a proposal amending its air pollution
regulations. On May 9, 2008, the Illinois Environmental Protection Agency (Agency or Illinois
EPA or IEPA) filed a proposal under the general rulemaking provisions of Sections 27 and 28 of
the Environmental Protection Act (Act) (415 ILCS 5/27, 28 (2008)). On both January 30, 2009,
and March 23, 2009, the Agency filed motions to amend the proposal. Generally, the Agency
proposes to amend Parts 211 and 217 of the Board’s air pollution regulations (35 Ill. Adm. Code
211, 217) to control nitrogen oxides (NO
x
) emissions from major stationary sources in the
nonattainment areas and from emission units including industrial boilers, process heaters, glass
melting furnaces, cement kilns, lime kilns, furnaces used in steelmaking and aluminum melting,
and fossil fuel-fired stationary boilers at such sources. On April 2, 2009, the Board granted the
Agency’s motion for expedited review of this proposal.
On May 7, 2009, the Board adopted its first-notice opinion and order in this proceeding.
See
33 Ill. Reg. 6896, 6921 (May 22, 2009). In that opinion and order, the Board largely adopted
the Agency’s proposal, including changes proposed in the two motions to amend.
In this opinion, the Board first provides the procedural history of this rulemaking before
addressing preliminary issues and background on regulation of NO
x
emissions. The Board then
addresses the public comments received since publication of the first-notice proposal. The Board
then discusses the issues raised during first notice before addressing economic reasonableness
and technical feasibility and summarizing the proposal on a section-by-section basis. Finally, the
order following the opinion then sets forth the proposed amendments for second notice.
PROCEDURAL HISTORY
On May 9, 2008, the Agency filed a rulemaking proposal (Prop.) under the general
rulemaking provisions of Sections 27 and 28 of the Act. 415 ILCS 5/27, 28 (2008). A Statement
of Reasons (Statement) and a Technical Support Document (TSD) accompanied the proposal. A
motion for waiver of copy requirements also accompanied the proposal. In an order dated June
5, 2008, the Board accepted the Agency’s proposal for hearing and granted the Agency’s motion
for waiver of copy requirements.

2
In a letter dated June 6, 2008, the Board requested that the Department of Commerce and
Economic Opportunity (DCEO) conduct an economic impact study of the Agency’s rulemaking
proposal.
See
415 ILCS 5/27(b) (2008). DCEO has not responded to the Board’s request.
In an order dated June 12, 2008, the hearing officer scheduled a first hearing to begin on
October 14, 2008, in Springfield and a second hearing to begin December 9, 2008, in Chicago.
The order directed participants wishing to testify at the first hearing to pre-file their testimony no
later than September 2, 2008. The order also directed participants to pre-file questions based on
the Agency’s pre-filed testimony no later than September 16, 2008. Finally, the order directed
the Agency to pre-file written answers to those pre-filed questions no later than September 30,
2008.
On August 29, 2008, the Agency pre-filed testimony by Mr. Robert Kaleel (Kaleel Pre-
filed Test.), Mr. Vir Gupta (Gupta Pre-filed Test.), and James E. Staudt, Ph.D. (Staudt Pre-filed
Test.).
On September 15, 2008, Midwest Generation filed questions for the Agency’s witnesses
(MG Questions). On September 16, 2008, ExxonMobil Oil Corporation (ExxonMobil) filed
questions for the Agency’s witnesses (ExxonMobil Questions). Also on September 16, 2008, the
Illinois Environmental Regulatory Group (IERG) filed questions for the Agency’s witnesses
(IERG Questions). On September 30, 2008, the Agency filed three documents: answers to
questions submitted by Midwest Generation (MG Answers); answers to questions submitted by
ExxonMobil (ExxonMobil Answers); and answers to questions submitted by IERG (IERG
Answers).
The first hearing took place as scheduled on October 14, 2008, in Springfield. At the first
hearing, the hearing officer admitted into the record four exhibits:
Finding of Failure to Submit State Implementation Plans Required for the 1997 8-Hour
Ozone NAAQS, 73 Fed. Reg. 15416-21 (Mar. 24, 2008) (Exh. 1);
[Illinois Environmental Protection] Agency Analysis of Economic and Budgetary Effects
of Proposed Rulemaking (35 Ill. Adm. Code 211) (Exh. 2);
[Illinois Environmental Protection] Agency Analysis of Economic and Budgetary Effects
of Proposed Rulemaking (35 Ill. Adm. Code 217) (Exh. 3); and
Cleaver Brooks letter dated May 19, 2006, to New Hampshire Division of Environmental
Services (Exh. 4).
On October 24, 2008, the Board received the transcript of the first hearing (Tr.1).
On November 5, 2008, the Agency filed its responses to questions raised at the first
hearing (PC 1).

3
On November 25, 2008, the Board received pre-filed testimony for the December 9,
2008, hearing from Mr. Scott Miller and Mr. Kent Wanninger on behalf of Midwest Generation,
from Ms. Deirdre K. Hirner and Mr. David J. Kolaz on behalf of IERG, from Mr. Larry G.
Siebenberger and Mr. Blake E. Stapper on behalf of U.S. Steel, and from Mr. David W. Dunn on
behalf of ConocoPhillips. Also on November 25, 2008, the Board received pre-filed comments
submitted by ArcelorMittal (ArcelorMittal Comment). In addition, on November 25, 2008, the
Board received post-hearing comments relating to the October 14, 2008 hearing from Saint-
Gobain Containers, Inc. (Saint-Gobain) (PC 2).
The second hearing took place as scheduled on December 9 and 10, 2008, in Chicago.
Over the two days of the second hearing, the hearing officer admitted into the record fourteen
exhibits:
Pre-Filed Testimony of Deirdre K. Hirner on Behalf of the Illinois Environmental
Regulatory Group (Exh. 5);
Pre-Filed Testimony of David J. Kolaz on Behalf of the Illinois Environmental
Regulatory Group (Exh. 6);
from Final Rule to Implement the 8-Hour Ozone National Ambient Air Quality
Standard; Final Rule, 70 Fed. Reg. 71657 (Nov. 29, 2005) (Exh. 7);
Summary of NO
x
Budget Allocations and Usage 2004-2007 (Exh. 8);
Pre-Filed Testimony of David W. Dunn on Behalf of ConocoPhillips Company (Exh. 9);
Pre-Filed Testimony of Larry G. Siebenberger on Behalf of United States Steel
Corporation (Exh. 10);
Pre-Filed Testimony of Blake E. Stapper on Behalf of United States Steel Corporation
(Exh. 11);
Testimony of Scott Miller of Behalf of Midwest Generation (Exh. 12);
Testimony of Kent Wanninger on Behalf of Midwest Generation (Exh. 13);
IHS-CERA Power Capital Costs Index (PCCI) (Graph Included on Page 7 of Kent
Wanninger’s Testimony on Behalf of Midwest Generation) (Exh. 14);
Baldwin 3 graph (Exh. 15);
Joliet 71 boiler graph (Exh. 16);
Bureau of Labor Statistics Producer Price Index. Commodities Group: Metals and metal
products Item: Hot rolled bars, plates, and structural shapes (December 4, 2008) (Exh.
17); and

4
Bureau of Labor Statistics Producer Price Index. Commodities Group: Metals and metal
products Item: Carbon scrap steel (Dec. 4, 2008) (Exh. 18).
On December 30, 2008, the Board received the transcript of December 10, 2008, the second day
of the second hearing (Tr.3). On January 5, 2009, the Board received the transcript of December
9, 2008, the first day of the second hearing (Tr.2).
In an order dated December 23, 2008, the hearing officer scheduled a third hearing for
February 3, 2009, in Edwardsville and directed participants wishing to testify at the third hearing
to pre-file testimony no later than January 20, 2009.
On January 20, 2009, the Board received post-hearing comments from IERG (PC 3),
Saint-Gobain (PC 4), and ConocoPhillips (PC 5). Also on January 20, 2009, the Board received
pre-filed testimony on behalf of the Agency from Mr. Robert Kaleel (Kaleel Pre-filed Test. 2),
Mr. Michael Koerber (Koerber Pre-filed Test.), and James E. Staudt, Ph.D. (Staudt Pre-filed
Test. 2). Also on January 20, 2009, the Agency filed a motion to correct the transcript of the
second hearing.
On January 30, 2009, the Agency filed a motion to amend its rulemaking proposal (Mot.
Amend 1).
On January 30, 2009, the Board received supporting materials from U.S. Steel. (PC 6).
On February 2, 2009, the Board received pre-filed testimony of Mr. Blake E. Stapper on behalf
of U.S. Steel. On February 3, 2009, the Board received a public comment from Mr. James L.
Kavanaugh of the Missouri Department of Natural Resources (PC 7).
The third hearing took place as scheduled on February 3, 2009, in Edwardsville. During
the third hearing, the hearing officer admitted into the record seven exhibits:
Western Michigan Ozone Study: Draft Report (January 21, 2009) (Exh. 19);
Calculation of Available COG after Consumption in Reheat Furnaces (Exh. 20);
Calculation of Siebenberger Exhibit A Information — COG burned in reheat furnaces per
Siebenberger December testimony (Exh. 21);
Total Boiler COG Usage from Attachment C (Exh. 22);
Calculation of Siebenberger Exhibit A Information — with 2008 COG rate, 35 day
scrubber maint. (Exh. 23);
Calculation of Siebenberger Exhibit A Information — with 2008 COG rate, no COG
scrubber maint. (Exh. 24); and

5
Pre-Filed Testimony of Blake E. Stapper on Behalf of United States Steel Corporation
(Exh. 25).
On February 11, 2009, the Board received the transcript of the third hearing (Tr.4).
In an order dated February 19, 2009, the Board granted the Agency’s motion to amend its
rulemaking proposal and also granted the Agency’s motion to correct the transcript of the second
hearing.
On March 19, 2009, the Agency filed a motion for expedited review. Also on March 19,
2009, the Agency forwarded to the Board’s Acting Chairman, Dr. G. Tanner Girard, a letter from
the United States Environmental Protection Agency (USEPA) (PC 8). On March 20, 2009, the
Board received Midwest Generation’s response to the Agency’s motion for expedited review.
On March 23, 2009, the Board received from Agency Director Douglas P. Scott a letter
regarding expedited review of the Agency’s amended proposal. On March 26, 2009, the Board
received IERG’s response to the Agency’s motion for expedited review. In an order dated April
2, 2009, the Board granted the Agency’s motion for expedited review.
On March 23, 2009, the Board received post-hearing comments from Midwest
Generation (PC 9), ArcelorMittal (PC 10), U.S. Steel (PC 12), IERG (PC 13), and
ConocoPhillips (PC 14). Also on March 23, 2009, the Board received post-hearing comments
from the Agency (PC 11), accompanied by the Agency’s second motion to amend its rulemaking
proposal (Mot. Amend 2).
On May 7, 2009, the Board issued its first notice opinion and order.
See
33 Ill. Reg.
6896, 6921 (May 22, 2009). Among other action, that opinion granted the Agency’s second
motion to amend its rulemaking proposal.
On July 1, 2009, the Board received a comment submitted by ArcelorMittal (PC 15). On
July 6, 2009, the Board received comments submitted by IERG (PC 16), the Agency (PC 17),
ConocoPhillips (PC 18), and U.S. Steel (PC 19). On July 7, 2009, ArcelorMittal filed a motion
for leave to file a response to the Agency’s first notice comment (Mot. Leave), accompanied by
its response (PC 20). On July 8, 2009 the Board received comments submitted by the U.S.
Department of Energy and the Argonne National Laboratory (collectively, Argonne) (PC 21).
On July 15, 2009, the Agency filed a motion for leave to file
instanter
a response to the first
notice comments of U.S. Steel and ArcelorMittal (Agency Mot.), accompanied by its response to
those comments (PC 22).
PRELIMINARY ISSUES
ArcelorMittal Motion for Leave to File Response
As noted immediately above, on July 7, 2009, ArcelorMittal filed a motion for leave to
file a response to the Agency’s first notice comment.
See
Mot. Leave, citing 35 Ill. Adm. Code
101.500, 101.502. ArcelorMittal requests that either the Board or the hearing officer allow it to
file the accompanying response. Mot. Leave at 1;
see
PC 20.

6
In support of its motion, ArcelorMittal states that it filed a first notice comment on July 1,
2009, and that the Agency filed a first notice comment on July 6, 2009. Mot. Leave at 1.
ArcelorMittal claims that the Agency’s comment “raised a few issues regarding cost
effectiveness and the appropriate NO
x
emission limit for other sources that ArcelorMittal feels
must be rebutted.”
Id
.
ArcelorMittal notes that the Illinois Administrative Procedure Act (APA) provides a first
notice comment period of at least 45 days and that the 45-day period ended July 6, 2009. Mot.
Leave at 1, citing 5 ILCS 100/5-40(b) (2008);
see
33 Ill. Reg. 6896, 6921 (May 22, 2009) (first
notice publication). ArcelorMittal notes that, while the Board has granted the Agency’s request
for expedited review of this proposal, the APA does not forbid a first notice comment period
longer than 45 days and the Board is not scheduled to meet until later in the month of July. Mot.
Leave at 1;
see
5 ILCS 100/5-40(b) (2008). ArcelorMittal requests that either the Board or the
hearing officer grant the motion in order “to prevent material prejudice to ArcelorMittal.” Mot.
Leave at 1. ArcelorMittal argues that “[n]o undue hardship on any party will occur by granting
this Motion.”
Id
. at 2.
Section 101.500(d) of the Board’s procedural rules provides in pertinent part that,
[w]ithin 14 days after service of a motion, a party may file a response to the
motion. If no response is filed, the party will be deemed to have waived objection
to the granting of the motion, but the waiver of objection does not bind the Board
or the hearing officer in its disposition of the motion. Unless undue delay or
material prejudice would result, neither the Board nor the hearing officer will
grant any motion before expiration of the 14 day response period except in
deadline driven proceedings where no waiver has been filed. 35 Ill. Adm. Code
101.500(d).
The Board notes that no participant has filed a response to ArcelorMittal’s motion for
leave to file a response. In the absence of a response and after reviewing the substance of the
motion, the Board grants the motion, accepts ArcelorMittal’s response, and summarizes it below.
See infra
at 23-24.
Agency Motion for Leave to File Response
As noted above under “Procedural History,” the Agency on July 15, 2009, filed a motion
for leave to file
instanter
a response to the first notice comments of U.S. Steel and ArcelorMittal.
See
Agency Mot. at 1, citing 35 Ill. Adm. Code 101.500, 102.402. The Agency notes that both it
and U.S. Steel filed first notice comments with the Board on July 6, 2009. Mot. Leave at 1. The
Agency reports that “[c]ounsel for the Illinois EPA has discussed U.S. Steel’s comments with
counsel for U.S. Steel, and there is no objection to the filing of this motion.”
Id
. The Agency
also notes that, on July 7, 2009, ArcelorMittal file a motion for leave to respond to the Agency’s
first notice comments, accompanied by its response.
Id
. at 2. As noted immediately above, the
Board has granted ArcelorMittal’s motion and accepted its response. The Agency states that it
“regrets the timing of this latest request,” but it “deems it necessary to respond to U.S. Steel’s

7
First Notice Comments and ArcelorMittal’s Response to the Illinois EPA’s First Notice
Comments.”
Id
. The Agency requests that the Board grant the motion for leave to file
instanter
.
As noted above, Section 101.500(d) of the Board’s procedural rules provides in pertinent
part that,
[w]ithin 14 days after service of a motion, a party may file a response to the
motion. If no response is filed, the party will be deemed to have waived objection
to the granting of the motion, but the waiver of objection does not bind the Board
or the hearing officer in its disposition of the motion. Unless undue delay or
material prejudice would result, neither the Board nor the hearing officer will
grant any motion before expiration of the 14 day response period except in
deadline driven proceedings where no waiver has been filed. 35 Ill. Adm. Code
101.500(d).
The Board notes that it has granted the Agency’s motion to expedite consideration of this
rulemaking proposal. In granting that motion, the Board cited USEPA’s implementation
deadline and the risk of federal sanctions in the event that the state does not meet that deadline.
In the Matter of: Nitrogen Oxides Emissions from Various Source Categories: Amendments to
35 Ill. Adm. Code Parts 211 and 217, R08-19, slip op. at 4 (Apr. 2, 2009). The Board thus finds
that undue delay would result from allowing the 14-day response period to run to July 29, 2009,
and proceeds to decide the motion. Having reviewed the substance of the motion, the Board
grants the motion for leave to file
instanter
, accepts the Agency’s response, and summarizes it
below.
See infra
at 24-26.
BACKGROUND ON REGULATION OF NO
x
EMISSIONS
NO
x
is one of the primary precursors to the formation of ozone and is also a precursor to
the formation of PM
2.5
.
1
Statement at 2, 3.
The Agency reports that, “[o]n July 18, 1997, USEPA revised the NAAQS [National
Ambient Air Quality Standard] for ozone by replacing the 1-hour standard with an 8-hour
standard.” Statement at 3, citing 62 Fed. Reg. 38856 (July 18, 1997). Illinois includes two areas
designated as nonattainment for the 8-hour ozone standard. Statement at 3. The Chicago
nonattainment area includes Cook, DuPage, Kane, Lake, McHenry, and Will Counties, Goose
Lake and Aux Sable Townships in Grundy County, and Oswego Township in Kendall County.
Id
. The Metro East nonattainment area includes Jersey, Madison, Monroe, and St. Clair
Counties.
Id.
at 3, 5.
The Agency also reports that, “[o]n July 18, 1997, USEPA revised the NAAQS for
particulate matter to add new standards for fine particles, using PM
2.5
as the indicator, and
established primary annual and 24-hour standards for PM
2.5
.” Statement at 4, citing 62 Fed. Reg.
38652 (July 18, 1997). The Agency states that USEPA has recently strengthened the 24-hour
standard. Statement at 4, citing 71 Fed. Reg. 61144 (Oct. 17, 2006). Illinois includes two areas
1
“PM
2.5
refers to particulate matter that is 2.5 micrometers or smaller in size.” Statement at 4.

8
designated nonattainment for the PM
2.5
standard. Statement at 4. The Chicago nonattainment
area includes Cook, DuPage, Kane, Lake, McHenry, and Will Counties, Goose Lake and Aux
Sable Townships in Grundy County, and Oswego Township in Kendall County.
Id
. at 4-5. The
Metro East nonattainment area includes Madison, Monroe, and St. Clair Counties and Baldwin
Township in Randolph County.
Id
. at 5, citing 40 C.F.R. § 81.314.
The Agency states that Section 110 of the Clean Air Act (CAA) and other related
provisions require states to submit for USEPA approval State Implementation Plans (SIP) “that
provide for the attainment and maintenance of standards established by USEPA through control
programs directed to sources of the pollutants involved.” Statement at 2, citing 42 U.S.C. §
7410. The Agency further states that “[t]he CAA also provides for the State to address emissions
sources on an area-specific basis through such requirements as reasonably available control
measures (“RACM”) and reasonable available control technology (“RACT”).” Statement at 2,
citing 42 U.S.C §§ 7502, 7511a. Specifically, the CAA requires Illinois for each nonattainment
area “to demonstrate that it has adopted ‘all reasonably available control measures as
expeditiously as possible (including such reductions in emissions from existing sources in the
area as may be obtained through the adoption, at a minimum, of reasonable available control
technology) and shall provide for attainment of the national primary ambient air quality
standards.’” Statement at 2, 5, citing 42 U.S.C. § 7502(c)(1).
The Agency characterizes RACT as “[a] subset of RACM.” Statement at 6, citing 44
Fed. Reg. 53762 (Sept. 17, 1979). The Agency states that “Section 182(b)(2) of the CAA
requires states to adopt RACT rules for all areas designated nonattainment for ozone and
classified as moderate or above.” Statement at 6-7, citing 42 U.S.C. § 7511a(b)(2). The Agency
further states that Section 182(f) of the CAA requires each state in which all or part of a
moderate nonattainment area is located to adopt RACT for major NO
x
sources. Statement at 7,
citing 42 U.S.C. § 7511a(f). The Agency notes that “Section 302 of the CAA defines ‘major
stationary source’ as any stationary facility or source of air pollutants that directly emits, or has
the potential to emit, one hundred tons per year or more of any air pollutant.” Statement at 7,
citing 42 U.S.C. § 7602.
The Agency argues that these authorities “establish the requirements for Illinois to submit
NO
x
RACT regulations for all major stationary sources of NO
x
in PM
2.5
nonattainment areas and
ozone nonattainment areas classified as moderate and above.” Statement at 7, citing 72 Fed.
Reg. 20586 (Apr. 25, 2007); 70 Fed. Reg. 71612 (Nov. 29, 2005). The Agency further argues
that, because Illinois includes nonattainment areas classified as moderate and above for the 8-
hour ozone NAAQS, it was “required to submit by September 15, 2006, a SIP demonstrating that
sources specified under the CAA were subject to RACT requirements.” Statement at 7-8, citing
70 Fed. Reg. 71612 (Nov. 29, 2005). The Agency claims that, “[o]n March 24, 2008, USEPA
made a finding that Illinois, among other states, failed to make a RACT submittal required under
Part D of Title I of the CAA for its two moderate nonattainment areas.” Statement at 8, citing 73
Fed. Reg. 15416 (Mar. 24, 2008). The Agency notes that “[s]uch finding starts the 18-month
emission offset sanctions clock and 24-month highway funding sanctions clock under Section
179(a) and (b) of the CAA and the 24-month clock for the promulgation by USEPA of a Federal
Implementation Plan under Section 110(c) of the CAA”. Statement at 8, citing 42 U.S.C. §§
7509(a) and (b), 7410(c).

9
In testimony for the third hearing, Mr. Kaleel stated that USEPA on December 22, 2008,
designated areas as nonattainment for the 24-hour PM
2.5
standard. Kaleel Pre-filed Test. 2 at 3.
He further stated that, in Illinois, USEPA has designated “the same areas designated previously
as nonattainment for the annual PM
2.5
standard.”
Id
. He added that “Illinois must develop an
attainment plan and adopt control measures needed to attain the 24-hour PM
2.5
standard within
three years of the effective date of U.S. EPA’s decision, and Illinois must attain the standards
within five years of the effective date.”
Id
.
Mr. Kaleel also addressed the establishment of nonattainment areas for the 2008 8-hour
ozone standard. He stated that the Agency’s “initial proposal is for Illinois to recommend to
USEPA to establish nonattainment boundaries for the 2008 standard that generally match the
boundaries already established for the 1997 ozone standard.” Kaleel Pre-filed Test. 2 at 3. He
anticipated that USEPA will complete nonattainment designations in 2010, “initiating a new
cycle of planning and regulatory development.”
Id
. at 3-4. He expects that, because NO
x
is a
precursor to both ozone and PM
2.5
, NO
x
emission reductions will improve air quality.
Id
. at 4.
He argues that “[t]he reductions provided by the subject NO
x
RACT proposal will help to meet
the new standards and should help to address any future requirements to implement RACT for
the new standards.”
Id
. Specifically, he claims that, “[u]nless USEPA issues new guidance
regarding NO
x
control technology, we expect that this RACT proposal will satisfy requirements
to implement NO
x
RACT under the revised NAAQS for the source categories and geographic
areas to which this proposal applies.” MG Answers at 1.
SUMMARY OF FIRST NOTICE COMMENTS
ArcelorMittal (PC 15)
Background
ArcelorMittal states that its facility located in Riverdale “has a roller-hearth tunnel
furnace equipped with ultra-low NO
x
burners (ULNBs), which processes thin cast steel slabs.”
PC 15 at 1. ArcelorMittal further states that “[t]he permitted NO
x
emission limit for the tunnel
furnace is 0.171 lb/mmBtu.”
Id
. ArcelorMittal notes that the Agency originally proposed a NO
x
emission limit of 0.05 lb/mmBtu for reheat furnaces (recuperative, combusting natural gas).
Id
.;
see
Prop. at 50 (proposed Section 217.144(a)(2)). ArcelorMittal also indicates that the Agency
has expressed the view that “ArcelorMittal’s tunnel furnace was subject to this emission limit for
reheat furnaces.” PC 15 at 1.
Technical Feasibility
ArcelorMittal states that, after it had participated in hearings and communicated with the
Agency about this proposed rule, “the Agency revised its proposed NO
x
emission limit for reheat
furnaces to 0.09 lb/mmBtu.”
Id
. at 2;
see
Mot. Amend 2 at 12. ArcelorMittal states that it has
not reached a concurrence with the Agency on the applicability of this proposed rule or on the
appropriate emissions limit. PC 15 at 2. ArcelorMittal argues that the Agency failed to justify
the amended limit of 0.09 lb/mmBtu either economically or technologically and also failed to

10
demonstrate that it is based on RACT. PC 15 at 2. ArcelorMittal requests that the Board
reconsider the amended emission limit of 0.09 lb/mmBtu “based on economic reasonableness,
technical feasibility and product quality issues.”
Id
.
In its post-hearing comments, the Agency stated that it had surveyed NO
x
emission limits
for recently-constructed furnaces similar to ArcelorMittal’s. PC 11 at 21;
see
PC 15 at 3; PC 15,
Exh. A (Table: Summary of NO
x
Emissions from Reheat Furnaces). ArcelorMittal distinguishes
furnaces cited by the Agency from its own. First, ArcelorMittal notes that the Agency’s survey
lists an emission limit of 0.0147 lb/mmBtu for the Beta Steel reheat furnace slab 2 in Porter
County, Indiana. PC 15 at 3; PC 15, Exh. A. ArcelorMittal states that it determined that that
limit “was the original permit limit based on manufacturer’s estimates, which the source
subsequently could not consistently meet.”
Id
. at 3. ArcelorMittal states that, based on Beta
Steel’s operating permit, the current emission limit for its reheat furnace is 0.077 lb/mmBtu. PC
15 at 3; PC 15, Exh. B (Indiana operating permit);
see
PC 20 at 2 n.1 (correcting original
reference to limit of 0.77 lb/mmBtu).
Second, ArcelorMittal states that the Nucor Steel facility in Tuscaloosa, Alabama differs
from its own facility, as Nucor has an equalizing furnace operating “much differently that (sic)
the tunnel furnace at Riverdale.” PC 15 at 3-4. In addition, ArcelorMittal states that Nucor
produces slabs five inches thick, while its own Riverdale facility produces slabs only two inches
thick.
Id
. at 4;
see
ArcelorMittal Comment at 2 (Nov. 25, 2008). ArcelorMittal also states that
the V&M Star facility in Mahoning County, Ohio differs from its own facility, as V&M Star has
a billet furnace operating “much differently” than a tunnel furnace. PC 15 at 3-4.
Third, ArcelorMittal states that two of the facilities summarized by the Agency, New
Steel International in Haverhill, Ohio and Minnesota Steel Industries, LLC in Itasca County,
Minnesota “have not been constructed to date.” PC 15 at 4;
see
PC 15, Exh. A. Finally,
ArcelorMittal argues that, although the Severstal Columbus facility in Columbus, Mississippi “is
similar to the Riverdale facility,” it has not yet been issued a final permit.
Id
. at 4. Also,
ArcelorMittal notes that the Severstal Columbus facility includes two tunnel furnaces, a factor
that may influence the emission limit.
Id
. ArcelorMittal argues that none of these three facilities
has demonstrated achievement of the emission limits cited by the Agency.
Id
.;
see id
., Exh A.
ArcelorMittal concludes that the Agency’s “reliance on outdated, erroneous, or never-applied-in-
practice emission limits for ‘similar sources’” casts doubt on the feasibility and appropriateness
of the proposed limit of 0.09 lb/mmBtu.
Id
.
Economic Reasonableness
Addressing the issue of economic reasonableness, ArcelorMittal notes that the Agency
had established costs in the range of $2,500 to $3,000 per ton of emissions reduced. PC 15 at 4,
5, citing Tr.1 at 165-66, 173-74, Tr.4 at 75. ArcelorMittal further notes that the Agency’s TSD
characterized as typical costs of $1,000 per ton reduced. PC 15 at 4, 5, citing TSD at 99.
Finally, ArcelorMittal notes that USEPA’s implementation of the 8-hour ozone implementation
rule considered costs of less than $2,000 per ton reduced as reasonable for the purposes of
RACT. PC 15 at 4, 5, citing 70 Fed. Reg. 71652, 71654 (Nov. 29, 2005). ArcelorMittal states
that it prepared its own economic analysis in order to determine the cost effectiveness based on

11
“next-generation” ULNBs now available. PC 15 at 5. That analysis determined a cost
effectiveness ranging from $22,895 to $39,472 per ton of NO
x
emissions reduced.
Id
.;
see
PC 10
at 6. ArcelorMittal emphasizes that these burner changes guaranteed emissions of 0.068
lb/mmBtu and 0.054 lb/mmBtu. PC 15 at 5;
see
PC 10, Exh. A. While ArcelorMittal
acknowledges that these guarantees are lower than the Agency’s proposed emission limit, it
argues that “this does not change the analysis that ArcelorMittal would have to install one of the
two next-generation burners to meet the proposed revised limit.” PC 15 at 5. Furthermore,
ArcelorMittal argues that these cost estimates “did not include yield cost impacts and the
associated cost of production downtime to convert the furnace” and also assumed that the
converted furnace could continue to meet product quality specifications.
Id
.
Operational Issues
ArcelorMittal expresses concern with the effect of changing burners on the operation of
the tunnel furnace and on slab quality. PC 15 at 5. ArcelorMittal argues that such a change
would involve the modification or replacement of numerous elements of the furnace.
Id
. at 5-6.
Furthermore, because its steel-making process is continuous and because of the lack of
redundancy in its operation, ArcelorMittal states that “the tunnel furnace must operate optimally
at all times.”
Id
. at 6. ArcelorMittal suggests that changing burners may jeopardize the
continuous operation and may undermine its investment in developing unique products.
See id
.
Summary
ArcelorMittal argues that that, because of operational and functional differences, its
tunnel furnace cannot be appropriately compared to other reheat furnaces. PC 15 at 6.
ArcelorMittal further argues that the Agency’s summary of emissions from other reheat furnaces
does not provide support for the Agency’s proposed emission limit.
Id
. ArcelorMittal
specifically requests that the Board “allow a source to be exempt from the proposed NO
x
emission limits upon an adequate demonstration that additional NO
x
controls would be
economically unreasonable.”
Id
. at 6-7. ArcelorMittal believes that it has made such a
demonstration “and requests utilization of the emission limit currently applicable and permitted
for the tunnel furnace” at its Riverdale facility.
Id
. at 7.
Agency (PC 17)
The Agency states that its first notice comments address two matters: proposing
corrections and clarifications to the first notice publication of the proposed rules, and responding
to the first notice comments filed by ArcelorMittal. PC 17 at 1;
see generally
PC 15. The Board
separately summarizes the Agency’s comments on those two matters in the following
subsections.
Corrections and Clarifications
The Agency first proposes to amend the definition of “industrial boiler” at proposed
Section 211.3100 “by striking the reference to ‘cogeneration units.’” PC 17 at 1-2, citing In the
Matter of: Nitrogen Oxides Emissions from Various Source Categories: Amendments to 35 Ill.

12
Adm. Code Parts 211 and 217, R08-19, slip op. at 26, 71 (May 7, 2009). Second, the Agency
proposes in Section 217.104 to update three incorporations by reference at subsections (l), (o),
and (p). PC 17 at 2. The Agency also seeks in proposed subsections (q) and (r) to incorporate by
reference additional materials.
Id
. The Agency attached to its comments a copy of the second
set of materials, “40 C.F.R. 60, Appendix B, Performance Specification 16, 74 Fed. Reg. 12575
(Mar. 25, 2009).” PC 17 at 2. Third, the Agency also seeks to “[a]mend the heading of Subpart
D of Part 217 by deleting the reference to ‘Industrial Boilers; and adding “NO
x
General
Requirements.’”
Id
.
Fourth, the Agency proposes to clarify Section 217.154, which addresses performance
testing, by amending “subsections (a) and (b) to add references to ‘emissions limitations under’
an applicable Subpart and to add the exclusion for a ‘predictive emission monitoring system, or
combustion tuning.’” PC 17 at 2-3. Fifth, in subsections (a) and (g) of Section 217.158, the
Agency seeks to correct a cross-reference to Section 217.150(a)(1).
Id
. at 3. Sixth, in Section
217.158(a)(2), addressing units that may not be included in an emissions averaging plan, the
Agency proposes to amend subsection (C) with additional language regarding enforceable
orders.
Id
.
Seventh, in Section 217.158 addressing emissions averaging plans, the Agency proposes
language for a new subsection (j). PC 17 at 3. Eighth, in Section 217.160, which addresses
applicability to industrial boilers, the Agency proposed to amend subsection (b) “by striking the
references to ‘cogeneration units’ and adding reference to boilers that ‘meet the applicability
criteria under Subpart M of Part 217.’”
Id
. at 4, citing In the Matter of: Nitrogen Oxides
Emissions from Various Source Categories: Amendments to 35 Ill. Adm. Code Parts 211 and
217, R08-19, slip op. at 45-46 (May 7, 2009). Ninth, in Section 217.164 addressing emissions
limitations for industrial boilers, that Agency proposes to amend the first paragraph with specific
language. PC 17 at 4.
Tenth, at Section 217.164(e), which provides an equation with which to determinate the
NO
x
emissions limitation for an industrial boiler combusting a combination of natural gas, coke
oven gas, and blast furnace gas, the Agency proposes to amend the denominator in the equation.
PC 17 at 4, citing In the Matter of: Nitrogen Oxides Emissions from Various Source Categories:
Amendments to 35 Ill. Adm. Code Parts 211 and 217, R08-19, slip op. at 98 (May 7, 2009);
see
also
PC 19 at 6 (U.S. Steel comment). Eleventh, at Section 217.184 addressing emissions
limitations for process heaters, the Agency proposes to amend the first paragraph with specific
language. PC 17 at 4. Twelfth, at Section 217.204 addressing emissions limitations for glass
melting furnaces, the Agency proposes to amend subsection (b) “due to the special
characteristics of glass melting and further discussions with Saint-Gobain.”
Id
. at 4-5.
Thirteenth, in Section 217.244 addressing iron and steel and aluminum manufacturing,
the Agency proposes to amend subsection (b) “by correcting emissions limitations” with specific
language. PC 17 at 5, citing In the Matter of: Nitrogen Oxides Emissions from Various Source
Categories: Amendments to 35 Ill. Adm. Code Parts 211 and 217, R08-19, slip op. at 105 (May
7, 2009). Fourteenth, in Section 217.340 addressing applicability to electrical generating units,
the Agency proposes specific language to add a “reference to any ‘fossil’ fuel-fired stationary
boiler serving ‘at any time’ a generator.” PC 17 at 5, citing In the Matter of: Nitrogen Oxides

13
Emissions from Various Source Categories: Amendments to 35 Ill. Adm. Code Parts 211 and
217, R08-19, slip op. at 55-56 (May 7, 2009). Fifteenth, in Section 217.342, addressing
exemptions for electrical generating units, the Agency proposed to amend subsection (b) in light
of a separate Board rulemaking docket. PC 17 at 5; citing Amendments to 35 Ill. Adm. Code
225: Control of Emissions from Large Combustion Sources (Mercury Monitoring), R09-10
(June 18, 2009) (final adoption). Finally, in Appendix H to Part 217, which provides compliance
dates for emission units at petroleum refineries, the Agency proposes corrections. PC 17 at 6.
Response to ArcelorMittal
The Agency states that ArcelorMittal’s first notice comments claim that the Agency
failed to justify its proposed revised emissions limitation and to demonstrate that it was based
upon RACT. PC 17 at 7, citing PC 15. The Agency counters that its TSD “provides detailed
performance and cost information that demonstrates that the proposed emissions limitations
contained in the rulemaking proposal are feasible technologically and economically.” PC 17 at
7, citing TSD. The Agency claims that “the NO
x
control technologies identified for reheat,
annealing and galvanizing furnaces at iron and steel plant are reasonably available, technically
feasible, and cost effective, even recognizing the tunnel design on ArcelorMittal’s reheat
furnace.” PC 17 at 7;
see
TSD at 92-101 (Reheat, Annealing and Galvanizing Furnaces at
Iron/Steel Plants).
The Agency indicates that ArcelorMittal has reviewed the summary of NO
x
emissions
limitations on which the Agency based its motion to amend the limitation for recuperative reheat
furnaces combusting natural gas. PC 17 at 7. The Agency seeks to counter ArcelorMittal’s
“attempts to distinguish itself from the sources surveyed.”
See id
. The Agency notes
ArcelorMittal’s claim that “the NO
x
emissions limitation for Beta Steel Corporation’s natural
gas-fired reheat furnace slab 2 of 0.0147 lb/mmBtu was the original permit limit based on the
manufacturer’s estimates, whereas the current permit limit is 0.77 lb/mmBtu.”
Id
., citing PC 15
at 3. The Agency argues that “[t]he permit limit that ArcelorMittal cites to is actually 0.077
lb/mmBtu, which is more stringent that the emissions limitation proposed by the Illinois EPA.”
PC 17 at 7.
The Agency also notes ArcelorMittal’s claim that neither the Nucor Steel facility in
Tuscaloosa, Alabama, nor the V&M Star facility in Mahoning County, Ohio, is similar to its own
facility. PC 17 at 7-8. The Agency further notes ArcelorMittal’s claim that neither the New
Steel International facility in Haverhill, Ohio, nor the Minnesota Steel Industries LLC facility in
Itasca County, Minnesota, has been constructed.
Id
. at 8. The Agency argues that “[e]missions
limitations set forth in construction permits are enforceable limits, and the actions of these states
to require such emission limits support the Illinois EPA’s proposal as technologically feasible for
this type of reheat furnace.”
Id
. at 8.
The Agency also addresses ArcelorMittal’s economic analysis and its “estimated cost
effectiveness for burner changes based upon the next-generation ultra low NO
x
burners currently
available.” PC 17 at 8, citing PC 10, Exh. A (filed March 23, 2009). The Agency expresses the
opinion that “the economic analysis provided by ArcelorMittal is flawed and should not be relied
upon as evidence that the proposed emission limits are beyond RACT from an economic

14
perspective.” PC 17 at 8. The Agency argues that ArcelorMittal relies on Series 1430 burners
designed in the 1980s that do not constitute “advanced NO
x
control technology.”
Id
.
The Agency notes that ArcelorMittal’s estimated cost effectiveness is $22,985 per ton of
NO
x
removed under one scenario and $39,472 under another.
Id
.,
see
PC 10, Exh. A. Noting
that ArcelorMittal’s scenarios are based upon a five-year equipment life, the Agency argues that
“the expected equipment life is much greater than five years, as the existing burners in
ArcelorMittal’s furnace are about 20 years old.” PC 17 at 8 (proposing 15-20 years expected
life). The Agency argues that, “[b]y using unreasonably low equipment life in the economic
analysis, ArcelorMittal has overstated the annualized costs of installing and maintaining the
controls needed to comply with the Illinois EPA’s proposal.”
Id
. The Agency further argues that
ArcelorMittal’s estimates rely on an interest rate of ten percent and a contingency of 20 percent,
both of which it characterizes as “high.”
Id
. The Agency claims that these high estimates also
overstate the costs of complying with its proposal.
Id
. at 8-9. On these grounds, the Agency
argues that “ArcelorMittal’s economic analysis should not be relied upon as evidence that the
proposed emission limits are beyond RACT.”
Id
. at 9.
The Agency also notes ArcelorMittal’s request that the Board propose for second notice
language that would “allow a source to be exempt from the proposed NO
x
emissions limitations
upon an adequate demonstration that additional NO
x
controls would be economically
unreasonable.” PC 17 at 9. The Agency argues that its proposal does not include the case-by-
case RACT determinations that ArcelorMittal apparently seeks.
Id
. The Agency states that it
“opposes the inclusion of such options in this proposal.”
Id
. The Agency notes that “[t]he
Board’s regulations include mechanisms for regulatory relief under specific circumstances” and
“acknowledges that sources may initiate proceedings for such relief.”
Id
.
U.S. Steel (PC 19)
U.S. Steel states that the proposed rulemaking would affect boilers, slab reheat furnaces,
and galvanizing lines at its Granite City Works (GCW). PC 19 at 1, citing Exh. 10 at 5 (pre-filed
testimony of Mr. Larry G. Siebenberger). U.S. Steel reports that, after participating in the
hearings and a series of discussions with the Agency, it reached agreement with the Agency on
determining NO
x
emission limits for Boilers 11 and 12 and slab furnaces 1 through 4. PC 19 at
2-3. Accordingly, U.S. Steel states that it “supported the Agency’s proposed amendments to the
rule as described in the Agency’s Second Motion to Amend Rulemaking Proposal and Post-
Hearing Comments filed with the Board on March 23, 2009.”
Id
. at 3;
see generally
Mot.
Amend 2. Nonetheless, U.S. Steel comments that it wishes to clarify the use of desulfurized
coke oven gas (“COG”) and “reiterate the need for revision to the proposed emission averaging
provisions to cover time periods when the desulfurization unit is shutdown due to unplanned
outages or upsets.” PC 19 at 3. U.S. Steel further comments that it proposes to amend the
proposed Section 217.157 so it is consistent with the construction permit for its cogeneration
boiler.
Id
.
Desulfurization Unit

15
U.S. Steel notes that, under the proposed subsection 217.158(i), “calculations for
determining NO
x
limits during the averaging period will not include periods when the COG
desulfurization unit is shut down for maintenance so long as certain conditions are met.” PC 19
at 3;
see
Mot. Amend 2 at 9. These conditions include advance notice of shutdown and a limit
on the number of shutdown days. PC 19 at 3; Mot. Amend 2 at 9. U.S. Steel states that, while
this proposed language works very well for planned maintenance, it does not adequately address
brief unplanned outages or upsets of the COG desulfurization unit. PC 19 at 3
.
U.S. Steel
restates its request that “the Board include a revision to the averaging provision to accommodate
such brief outages and upsets, as well as startups and shutdowns, of the COG desulfurization
unit.”
Id
. at 3-4;
see
PC 12 at 3 (post-hearing comment). Because the unit will not operate
during those periods, U.S. Steel argues that, like planned maintenance shutdowns, they should
not be included in averaging calculations. PC 19 at 4.
U.S. Steel again stresses that it has not completed construction of its COG desulfurization
unit. PC 19 at 4. U.S. Steel also stresses that “the proposed emission limitations are based on
desulfurized COG having an
estimated
concentration of hydrogen cyanide or HCN of 130 ppm
or less.”
Id
. (emphasis in original). U.S. Steel thus states that “[t]he limitations associated with
the use of desulfurized COG will have to be revisited once construction of the COG
desulfurization unit is complete, if the actual concentration of HCN is greater than 130 ppm.”
Id
.
U.S. Steel expresses the understanding that a change in the rules may be necessary after it
completes construction of the COG desulfurization unit.
Id
.
Emissions Monitoring
U.S Steel states that proposed Section 217.157(a)(1) “requires that owners or operators of
industrial boilers that are greater than 250 mmBtu/hr install and operate a continuous emissions
monitoring system (“CEMS”) to measure NO
x
emission in accordance with 40 C.F.R. Part 75.”
PC 19 at 4;
see
Prop. at 32. U.S. Steel further states that it “is constructing a blast furnace gas
cogeneration boiler with a heat input capacity of 505 mmBtu/hr.” PC 19 at 4;
see
PC 19, Att. A
at 10 (construction permit § 3.1.2). U.S. Steel argues that, if Section 217.157(a)(1) is adopted as
proposed, its cogeneration boiler will be subject to the CEMS requirement. PC 19 at 4.
U.S. Steel claims, however, that this requirement conflicts with the construction permit
issued by the Agency. PC 19 at 4;
see id
., Att. A. Specifically, U.S. Steel states that condition
3.1.8-1(a) of that permit provides that
the Permittee shall install, calibrate, operate, and maintain NO
x
and CO
continuous monitoring system(s) on the affected unit within one year after the
initial emission testing required by this permit unless this testing or further testing
conducted by the Permittee demonstrates that the unit normally complies by a
margin of at least 5 percent with the NO
x
and CO emission limit in this permit or
the Illinois EPA approves further time for the Permittee to achieve this level of
performance.
Id
. at 4-5, citing
id
., Att. A at 15.
U.S. Steel argues that the Board should amend proposed Section 217.157(a) to exempt the
cogeneration boiler from the requirements of that section “so long as U.S. Steel complies with

16
the terms of the construction permit issued for such boiler.”
Id
. at 5. Specifically, U.S. Steel
proposed that the Board add the following language to the proposed Section 217.157(a):
[t]he owner or operator of an industrial boiler combusting blast furnace gas
subject to Subpart E of this Part with a rated heat input capacity greater than 500
mmBtu/hr located at a source that manufactures iron or steel must install,
calibrate, operate, and maintain continuous monitoring systems on the emission
unit within one year after the initial emission testing required by the state
construction permit issued by the Agency for the emission unit, unless this testing
or further testing conducted by the owner or operator of the emission unit
demonstrates that the emission unit normally complies by a margin of at least 5
percent with the NO
x
emission limit in the state construction permit issued by the
Agency for the emission unit or the Agency approves further time for the owner
or operator to achieve this level of performance. PC 19 at 5.
U.S. Steel also argues that, if the Board adopts this additional language, the Board should also
include a cross-reference to it in the proposed Section 217.157(a)(1).
Id
. at 5-6.
ConocoPhillips (PC 18)
ConocoPhillips states that the proposed rule would establish NO
x
RACT limits applicable
to sources “including many of the boilers and process heaters” at its Wood River Refinery. PC
18 at 1. ConocoPhillips refers to its post-hearing comments, in which it described “two
remaining concerns with the Agency’s proposed rule.”
Id
., citing PC 14 at 2-3.
ConocoPhillips states that it has continued to work with the Agency to “resolve several
issues related to maintenance turnarounds for NO
x
pollution control equipment and the inclusion
of boilers and process heaters in emission averaging plans.” PC 18 at 2. ConocoPhillips further
states that it has “reached agreement with the Agency on these issues.”
Id
. at 2-3. Consequently,
“ConocoPhillips supports the Agency’s proposed amendments to the rule as described in the
Agency’s First Notice Comments.”
Id
. at 3;
see
PC 17 at 3 (proposing correction and
clarification of Section 217.158).
IERG (PC 16)
IERG states that, while the rulemaking process has addressed many of its questions and
concerns, it wishes to address a few remaining matters. PC 16 at 1-3, citing PC 13 at 3-8 (IERG
post-hearing comment). In addition, IERG states that it seeks “clarification of certain provisions
based on discussions held with its Members following issuance of the First Notice Opinion and
Order.” PC 16 at 3. The Board addresses these issues in the subsections below.
Emissions Limits
IERG concurs with the Board’s opinion that the Agency has explained in detail how the
twice-amended rulemaking proposal is RACT for NO
x
. PC 16 at 3, citing In the Matter of:
Nitrogen Oxides Emissions from Various Source Categories: Amendments to 35 Ill. Adm. Code

17
Parts 211 and 217, R08-19, slip op. at 20 (May 7, 2009). IERG notes the Agency’s indication
that “it intends the NO
x
RACT rule to ‘provide a floor,’
i.e.
, a minimum emission limit, that a
new unit in the nonattainment areas can be expected to be required to meet.” PC 16 at 4, citing
PC 11 at 19-20. IERG also notes that the Board has stated that the proposed standards may
provide a “benchmark for future emission sources that may be located in the nonattainment
areas.” PC 16 at 4, citing In the Matter of: Nitrogen Oxides Emissions from Various Source
Categories: Amendments to 35 Ill. Adm. Code Parts 211 and 217, R08-19, slip op. at 19 (May 7,
2009).
IERG acknowledges that benchmarks have value but expresses the concern that, if a
benchmark becomes a RACT ‘floor,’ it may complicate permitting for new sources. PC 16 at 4.
IERG generally agrees with the Agency that “new source permitting should, in theory, result in
more strict requirements than a RACT rule.”
Id
., citing PC 11 at 20. Nonetheless, IERG argues
that a site-specific analysis to determine the level of NO
x
control technology constituting BACT
or LAER for a new source could yield an emissions limitation less stringent than a RACT
‘floor.’ PC 16 at 4. Expressing uncertainty regarding the Agency’s application of such a
“floor,” IERG states that it “raises this issue so that the Board may be aware of the likelihood
that some sources may require the Board’s consideration of site-specific relief at a future date.”
Id
.
Compliance Date
IERG argues that a compliance date of January 1, 2014, would provide a greater
“opportunity for planning and financing any necessary modifications to facilities.” PC 16 at 4.
Nonetheless, “IERG acknowledges the validity of the Agency’s arguments for adoption of the
2012 [compliance] date, particularly in regard to the impact these rules are intended to have on
the newest ozone standard and the PM
2.5
daily standard.”
Id
. at 4-5. On this issue, IERG
expresses its appreciation for “the Agency’s stated willingness to work with impacted facilities
to achieve compliance in an appropriate and timely manner.”
Id
. at 5.
Averaging Provisions
IERG expresses substantial agreement with the Board’s revision of Section
217.158(a)(1)(C), addressed by both IERG and the Agency, regarding replacement units in
emissions averaging plans. PC 16 at 5, citing In the Matter of: Nitrogen Oxides Emissions from
Various Source Categories: Amendments to 35 Ill. Adm. Code Parts 211 and 217, R08-19, slip
op. at 41-42, 92 (May 7, 2009). To improve the clarity of that subsection, IERG proposes in the
fifth line to add a comma after “capacity” as follows:
C)
Units that commence operation after January 1, 2002, if the unit replaces
a unit that commenced operation on or before January 1, 2002, or it
replaces a unit that replaced a unit that commenced operation on or
before January 1, 2002. The new unit must be used for the same purpose
and have substantially equivalent or less process capacity, or be permitted
for less NO
x
emissions on an annual basis than the actual NO
x
emissions
of the unit or units that are replaced. Within 90 days after permanently

18
shutting down a unit that is replaced, the owner or operator of such unit
must submit a written request to withdraw or amend the applicable permit
to reflect that the unit is no longer in service before the replacement unit
may be included in an emissions averaging plan. PC 16 at 5, citing 33 Ill.
Reg. 6955 (May 22, 2009);
see
In the Matter of: Nitrogen Oxides
Emissions from Various Source Categories: Amendments to 35 Ill. Adm.
Code Parts 211 and 217, R08-19, slip op. at 92 (May 7, 2009).
In addition, IERG notes that the first notice version of subsection 217.158(d), addressing
updates to emissions averaging plans, provides that,
1)
If a unit that is listed in an emission averaging plan is taken out of service,
the owner or operator must submit to the Agency, within 30 days of such
occurrence, an updated emissions averaging plan; or
2)
If a unit that was exempt from the requirements of Subpart E, F, G, H, I,
or M of this Part pursuant to Section 217.162, 217.182, 217.202, 217.222,
217.242, or 217.342, of this Part, as applicable, no longer qualifies for an
exemption, the owner or operator may amend its existing averaging plan
to include such unit within 30 days after the unit no longer qualifies for the
exemption. PC 16 at 6, citing 33 Ill. Reg. 6956;
see
In the Matter of:
Nitrogen Oxides Emissions from Various Source Categories:
Amendments to 35 Ill. Adm. Code Parts 211 and 217, R08-19, slip op. at
43, 93 (May 7, 2009).
IERG argues that, in the absence of a specific definition, “taking a unit out of service for a brief
period of time for routine maintenance and repair could require modifying an emissions
averaging plan.” PC 16 at 6. IERG further argues that emissions averaging equations account
for time during which a unit is not operating or is out of service, “whether for routine
maintenance or repair, or due to operational requirements.”
Id
. IERG also argues that the
computation accounts for a unit that is “permanently shut down.”
Id
. Accordingly, IERG
suggests that the Board delete Section 217.158(d)(1) as “unnecessary.”
Id
.
In the event that the Board regards the subsection as necessary for recordkeeping, IERG
proposes alternative language under which “the requirement to update an emission averaging
plan would apply only to units that are ‘permanently shut down:’
1)
If a unit that is listed in an emissions averaging plan is permanently shut
downtaken out of service, the owner or operator must submit to the
Agency, within 390 days of such occurrence, an updated emissions
averaging plan; or. PC 16 at 6.
Regarding Section 217.158(d)(2), IERG states that the provision “allows units that were
previously exempt to be included in an averaging plan by amending the plan ‘within 30 days
after the unit no longer qualifies for the exemption.’” PC 16 at 7. IERG argues that this
language does not clearly indicate whether, if an owner or operator does not update the averaging

19
plan within 30 days, the owner or operator can include the unit in the plan after that 30-day
period has elapsed.
Id
. IERG further argues that “[o]nce a unit is no longer exempt, it is subject
to all of the applicable provisions of the proposed rule, and there should be no need for a time
limit for including such units in an emission averaging plan.”
Id.
Next, IERG claims that, consistent with the Agency’s intent, “this language is to describe
exceptions to the once-per-year limit to amending emission averaging plans contained in the
proposed [Section] 217.158(c).” PC 16 at 7. Accordingly, IERG proposed that the board amend
Section 217.158(d)(2) as follows:
2)
If a unit that was exempt from the requirements of Subpart E, F, G, H, I, or
M of this Part pursuant to Section 217.162, 217.182, 217.202, 217.222,
217.242, or 217.342, of this Part, as applicable, no longer qualifies for an
exemption, the owner or operator may amend its existing averaging plan at
any time to include such unit within 30 days after the unit no longer
qualifies for the exemption. PC 16 at 7.
IERG states that the proposed Section 217.158(h) “would allow exclusion from the
‘calculation demonstrating compliance’ certain time periods when a unit is shut down for a
maintenance turnaround.” PC 16 at 7;
see
In the Matter of: Nitrogen Oxides Emissions from
Various Source Categories: Amendments to 35 Ill. Adm. Code Parts 211 and 217, R08-19, slip
op. at 44, 96 (May 7, 2009). IERG further states that, “[i]n order to rely on the proposed
exemption, an owner/operator would have to notify the Agency in writing in advance,
and
the
shut down must not exceed 45 days per ozone season or calendar year.” PC 16 at 7 (emphasis in
original). IERG requests that the Board clarify this provision by revising it so that it “does not
restrict that a shut down of a covered unit during an actual maintenance turnaround be limited to
45 days, but that, instead, the exemption from the calculation demonstrating compliance would
be limited to 45 days.”
Id
. at 7-8. IERG stresses that, particularly at a large facility such as a
petroleum refinery, a planned maintenance turnaround may extend beyond 45 days because of
“delays associated with weather, manpower and equipment availability, as well as unplanned or
unforeseen mechanical setbacks.”
Id
. at 8. Accordingly, IERG proposes to amend Section
217.158(h) as follows:
h)
The owner or operator of an emission unit located at a petroleum refinery
who is demonstrating compliance with an applicable Subpart through an
emissions averaging plan under this Section may exclude from the
calculation demonstrating compliance those time periods when an
emission unit included in the emissions averaging plan is shut down for a
maintenance turnaround, provided that such owner or operator notify the
Agency in writing at least 30 days in advance of the shutdown of the
emission unit for the maintenance turnaround and the shutdown of the
emission unit does not exceed 45 days per ozone season or calendar year
and NO
x
pollution control equipment, if any, continues to operate on all
other emission units operating during the maintenance turnaround. This
provision is in no way intended to restrict to 45 days or less the shutdown

20
of a covered unit during a maintenance turnaround.
Id
., citing 33 Ill. Reg.
6959.
Types of Units Not in Nonattainment Areas
IERG states that it has repeatedly raised the concern that the Agency’s proposal
“establishes emissions limits for units that are not present in the nonattainment areas subject to
this proposal”. PC 16 at 8, citing PC 13 at 8; IERG Questions at 4; Tr.1 at 57-64. IERG
continues to consider these proposed limits as inappropriate, arguing that “[t]he owners and
operators of units potentially impacted under this proposal have not had the opportunity to
participate in this rulemaking.” PC 16 at 9. Specifically, IERG expresses the concern that,
“[c]onsidering unit-specific factors, a detailed case-by-case analysis for a particular unit could
show that, for that unit, the proposed emission limit does not reflect the application of
‘reasonably available control technology.’”
Id.
IERG also expresses the concern that that
proposed limits may serve as a “‘RACT floor’ for those units located outside of the
nonattainment areas, whose owners and operators have not had opportunity for unit-specific
discussions with Illinois IEPA during the course of this proceeding.”
Id
. at 9-10. IERG
expresses its “strong position that the emissions limits contained in the proposal should not be
interpreted to represent what is ‘reasonably available control technology.’”
Id
. at 10. IERG
argues that “[s]uch implications may not have been addressed in this proceeding, and may call
for establishing different emissions limits.”
Id
.
Reporting Requirements
Proposed Section 217.156(j) provides in part that “[t]he owner or operator of an emission
unit subject to the requirements of this Subpart and demonstrating compliance through the use of
a continuous emissions monitoring system must submit to the Agency a report within 30 days
after the end of each calendar quarter.” In the Matter of: Nitrogen Oxides Emissions from
Various Source Categories: Amendments to 35 Ill. Adm. Code Parts 211 and 217, R08-19, slip
op. at 36, 86 (May 7, 2009). IERG notes that proposed subsections (j)(1) and (j)(2) require that
those reports include two specified items:
1)
Information indentifying and explaining the times and dates when
continuous emissions monitoring for NO
x
was not in operation, other than
for purposes of calibrating or performing quality assurance or quality
control activities for the monitoring equipment; and
2)
An excess emissions and monitoring systems performance report in
accordance with the requirements of 40 C.F.R. 60.7(c) and (d) and 60.13,
or 40 C.F.R. 75, or an alternate procedure approved by the Agency and
USEPA. PC 16 at 10-11, citing 33 Ill. Reg. 6948 (May 22, 2009);
see
In
the Matter of: Nitrogen Oxides Emissions from Various Source
Categories: Amendments to 35 Ill. Adm. Code Parts 211 and 217, R08-
19, slip op. at 36, 86 (May 7, 2009).
IERG proposes to delete subsection (j)(1) and to amend subsection (j)(2) as follows:

21
2)
An excess emissions and monitoring systems performance report and/or
summary report in accordance with the requirements of 40 C.F.R. 60.7(c)
and (d) and 60.13, or 40 C.F.R. 75.73(f), or an alternate procedure
approved by the Agency and USEPA. PC 16 at 11.
IERG argues that the provisions of the Code of Federal Regulations (CFR) cited in proposed
subsection (j)(2) embody “[t]he fundamental requirements of subsection (j)(1).”
Id
. IERG
argues that “[t]hose CFR references provide, among other things, the criteria and reporting detail
for reporting continuous emissions monitoring down time, which are not included in subsection
(j)(1).”
Id
. IERG claims that striking subsection (j)(1) “would avoid the potential for confusion
resulting from the CFR reference included in [subsection] (j)(2).”
Id
.
IERG cites clarity and correctness in proposing to revise subsection (j)(2). PC 16 at 11.
First, IERG argues that, “[t]he reference to 40 C.F.R. 60.13 pertains to Monitoring
Requirements, and not recordkeeping and reporting, and thus should be excluded.”
Id
. Second,
IERG states that 40 C.F.R. 60.7(c) and (d) do address the report that is the subject of subsection
(j)(2).
Id
. Third, IERG claims that “40 C.F.R. 75.73(f) refers specifically to the quarterly
reporting requirements within the recordkeeping and reporting provisions of 40 C.F.R. 75.73,
which is the topic of proposed Section 217.156(j).”
Id
. IERG argues that “[t]he general
requirements for continuous emissions monitoring pursuant to 40 C.F.R. Part 75 are already
referenced in the proposed rule in Section 217.157 (Testing and Monitoring).
Id.
;
see
In the
Matter of: Nitrogen Oxides Emissions from Various Source Categories: Amendments to 35 Ill.
Adm. Code Parts 211 and 217, R08-19, slip op. at 36-40, 86-91 (May 7, 2009) (proposed Section
217.157).
Corrections
IERG states that a comparison of the proposed amendments in Board’s first notice order
and those published in the
Illinois Register
shows differences between those two versions. PC
16 at 12. IERG lists those that it believes may be substantive in nature.
Id
. The Board below
summarizes particular corrections proposed by IERG.
IERG notes that, although the Board’s table of contents for Part 217 amends the title of
Section 217.141, the
Illinois Register
does not reflect that change in the table of contents,
although it reflects the amended title elsewhere. PC 16 at 12;
compare
In the Matter of:
Nitrogen Oxides Emissions from Various Source Categories: Amendments to 35 Ill. Adm. Code
Parts 211 and 217, R08-19, slip op. at 72 (May 7, 2009)
and
33 Ill. Reg. 6931, 6939 (May 22,
2009). IERG also notes that the Board’s Section 217.141(c) contains specific language that does
not appear in the
Illinois Register
. PC 16 at 12;
compare
In the Matter of: Nitrogen Oxides
Emissions from Various Source Categories: Amendments to 35 Ill. Adm. Code Parts 211 and
217, R08-19, slip op. at 79-80 (May 7, 2009)
and
33 Ill. Reg. 6940. Also, IERG states that
“Section 217.141(d)(1) differs in the two versions.” Specifically, IERG notes that the Board in
that subsection changes “sources” to “units,” but the
Illinois Register
does not. PC 16 at 13;
compare
In the Matter of: Nitrogen Oxides Emissions from Various Source Categories:

22
Amendments to 35 Ill. Adm. Code Parts 211 and 217, R08-19, slip op. at 80 (May 7, 2009)
and
33 Ill. Reg. at 6941.
IERG states that the
Illinois Register
has titled Subpart D as “Industrial Boilers” and
suggests that it should instead be titled “NO
x
General Requirements.” PC 16 at 13, citing In the
Matter of: Nitrogen Oxides Emissions from Various Source Categories: Amendments to 35 Ill.
Adm. Code Parts 211 and 217, R08-19, slip op. at 80 (May 7, 2009); 33 Ill. Reg. 6941. IERG
also states that Section 217.154(d) addressing performance testing also differs between the two
versions. PC 16 at 13. IERG argues that this difference may generate some confusion about
whether the 30-day and five-day notice of performance testing must both be in writing.
Id
.
IERG claims that, in Section 217.164(e), the equation for calculating the NO
x
emissions
limitation for an industrial boiler combusting a combination of natural gas, coke oven gas, and
blast furnace gas, the
Illinois Register
versions “is missing the subscript ‘BFG’ and closing
parenthesis.” PC 16 at 13, citing In the Matter of: Nitrogen Oxides Emissions from Various
Source Categories: Amendments to 35 Ill. Adm. Code Parts 211 and 217, R08-19, slip op. at 98
(May 7, 2009); 33 Ill. Reg. 6962;
see
PC 17 at 4 (Agency comment). IERG also notes that, in
Section 217.244(b) addressing emissions limitations for iron and steel and aluminum
manufacturing, the two versions provide different limitations. PC 16 at 13-14, citing In the
Matter of: Nitrogen Oxides Emissions from Various Source Categories: Amendments to 35 Ill.
Adm. Code Parts 211 and 217, R08-19, slip op. at 105 (May 7, 2009); 33 Ill. Reg. 6970. Finally,
IERG notes that the two versions Appendix H, providing compliance dates for certain emissions
units at petroleum refineries, differ in specific aspects. PC 16 at 14, citing In the Matter of:
Nitrogen Oxides Emissions from Various Source Categories: Amendments to 35 Ill. Adm. Code
Parts 211 and 217, R08-19, slip op. at 106-07 (May 7, 2009); 33 Ill. Reg. 6972-73.
Summary
Noting the Agency’s motion to expedite consideration of its proposal, IERG expresses
support for adopting amendments on a schedule that avoids the risk of federal sanctions. PC 11
at 14. IERG suggests that that schedule allows the Board to give due consideration to the issues
raised in its comments.
See id
. IERG states that, beyond those issues, it “can offer its support
for the amendments as proposed at first-notice.”
Id
.
Department of Energy/Argonne National Laboratory (PC 21)
Argonne states that it has “identified a number of inconsistencies with respect to
industrial boilers (Subpart E) with a rated heat input capacity of less than or equal to 100
mmBtu/hr.” PC 21 at 1. Argonne notes that these boilers are required to perform combustion
tuning instead of meeting a numeric NO
x
emission limit.
Id
.;
see
In the Matter of: Nitrogen
Oxides Emissions from Various Source Categories: Amendments to 35 Ill. Adm. Code Parts 211
and 217, R08-19, slip op. at 98-99 (May 7, 2009) (proposed Section 217.166). Argonne states
that it has identified inconsistencies pertaining to proposed requirements for performance testing,
CEMS, and predictive emission monitoring systems (PEMS). PC 21 at 1.

23
Specifically, Argonne notes that the proposed Section 217.154(a) “requires performance
testing for all industrial boilers regardless of size, unless they employ CEMS.” PC 21;
see
In the
Matter of: Nitrogen Oxides Emissions from Various Source Categories: Amendments to 35 Ill.
Adm. Code Parts 211 and 217, R08-19, slip op. at 82 (May 7, 2009) (proposed Section 217.154).
Argonne states that, “[f]or boilers less than or equal to 100 mmBtu/hr rated heat input
demonstrating compliance through an emissions averaging plan and not using CEMS, Section
217.157(a)(4) requires performance testing, but that section does not address boilers less than or
equal to 100 mmBtu/hr rated heat input where emissions averaging is not used.” PC 21 at 1;
see
In the Matter of: Nitrogen Oxides Emissions from Various Source Categories: Amendments to
35 Ill. Adm. Code Parts 211 and 217, R08-19, slip op. at 87-88 (May 7, 2009).
Argonne continues by stating that “Section 217.157(a)(5) indicates that boilers less than
or equal to 100 mmBtu/hr rated heat input may use CEMS in place of emissions averaging under
Section 217.157(a)(4), but since there is no numeric NO
x
limit specified for such boilers in
Section 217.164, the use of CEMS would appear to be of little value.” PC 21 at 1.;
see
In the
Matter of: Nitrogen Oxides Emissions from Various Source Categories: Amendments to 35 Ill.
Adm. Code Parts 211 and 217, R08-19, slip op. at 87-88, 97-98 (May 7, 2009). Argonne also
claims that, “[s]imilarly, the use of PEMS specified in Section 217.157(f) for boilers less than or
equal to 100 mmBtu/hr rated heat input to show compliance to a non-numeric limit (combustion
tuning) would also seem unnecessary.” PC 21 at 1;
see
In the Matter of: Nitrogen Oxides
Emissions from Various Source Categories: Amendments to 35 Ill. Adm. Code Parts 211 and
217, R08-19, slip op. at 91 (May 7, 2009).
Argonne requests clarification of the inconsistencies that it cites. PC 21 at 1. Argonne
also proposes two specific revisions regarding industrial boilers with a rated heat input less than
or equal to 100 mmBtu/hr for which combustion tuning is required.
Id
.;
see
In the Matter of:
Nitrogen Oxides Emissions from Various Source Categories: Amendments to 35 Ill. Adm. Code
Parts 211 and 217, R08-19, slip op. at 97-97 (May 7, 2009) (proposed Section 217.164).
Argonne first proposes “that performance testing not be required.” PC 21 at 1. Second, Argonne
proposes that “the use of CEMS or PEMS also not be required (although this could be employed
at the option of the facility,
e.g.
, if the facility chose to use emissions averaging).”
Id
.
RESPONSES TO FIRST NOTICE COMMENTS
ArcelorMittal Response to Agency Comment
ArcelorMittal notes that its economic analysis of the cost effectiveness of a burner
change for the tunnel furnace at its facility “assumed a 5-year equipment life and a contingency
factor of 20%.” PC 20 at 1. ArcelorMittal emphasizes that, in relying on these assumptions, it
used figures published by USEPA and so noted in its analysis.
Id
.;
see
PC 10, Exh. A.
Responding to the Agency, ArcelorMittal states that it revised that analysis by assuming a 15-
year equipment life and a contingency of ten percent. PC 20 at 2. ArcelorMittal reports that this
revised analysis “indicates a cost-effectiveness of $10,348/ton of NO
x
removed for a next-
generation 1500 burner and a cost-effectiveness of $17,841/ton of NO
x
removed for a 1550
burner.”
Id
. , Exh. A. ArcelorMittal argues that these figures are “well in excess” of the range of
costs provided by the USEPA, the Agency, and the Technical Support Document.
Id
.

24
ArcelorMittal also replies to the Agency’s comments regarding emissions limits for other
sources.
See
PC 17 at 7-8. The Agency had indicated an emissions limit of 0.0147 lb/mmBtu
applicable to the Beta Steel facility in Porter County, Indiana. PC 20 at 2;
see
PC 17 at 7.
ArcelorMittal’s comment stated that this figure was based on a manufacturer’s estimate and that
the actual permitted level is 0.077 lb/mmBtu. PC 15 at 3, PC 20 at 2. ArcelorMittal
acknowledges the Agency’s comment that this permitted level is lower than the 0.09 lb/mmBtu
limit included in its proposal. PC 20 at 2. ArcelorMittal argues that, because the Agency erred
in listing the emissions limit applicable to this facility, it casts doubt on the Agency’s proposed
limit for reheat furnaces.
Id
.
ArcelorMittal argues that the Agency has failed to demonstrate that its proposal is both
economically reasonable and technically feasible with regard to reheat furnaces. PC 20 at 3.
ArcelorMittal requests that the Board determine that the current permitted emissions limit of
0.171 lb/mmBtu applicable to its Riverdale facility constitutes RACT.
Id
. ArcelorMittal further
argues that it would “conserve the time and resources of all parties by not requiring
ArcelorMittal to initiate a proceeding for subsequent regulatory relief.”
Id
.
Agency Response to U.S. Steel and ArcelorMittal Comments
U.S. Steel
The Agency first notes that U. S. Steel proposed to revise emissions averaging provisions
“to cover time periods when the coke oven gas desulfurization unit is shutdown due to unplanned
outages or upsets, as well as startups and shutdowns.” PC 22 at 1, citing PC 19 at 3-4, PC 12 at
4. The Agency states that “[o]peration during periods of malfunction, breakdown, and startup
are addressed under current Board regulations.” PC 22 at 1, citing 35 Ill. Adm. Code 201.261 –
201.265. The Agency claims that, in the course of its permitting process, it routinely addresses
operation during these periods by applying these regulations. PC 22 at 1-2. Accordingly, the
Agency supports the proposed Section 217.158(i), addressing planned maintenance cycles,
without further amendment.
Id.
at 2.
Second, the Agency addresses U.S. Steel’s comment “regarding the emissions limitation
for a recuperative reheat furnace combusting a combination of natural gas and coke oven gas that
is based upon desulfurized coke oven gas having an estimated concentration of hydrogen cyanide
of 130 parts per million or less. . . .” PC 22 at 2. U.S. Steel also raised the possibility that, once
it completes construction and begins operation of the coke oven gas desulfurization unit, it may
need to seek revision of the applicable emissions limit.
Id
.;
see
PC 19 at 3-4. The Agency states
that it “agrees with U.S. Steel and acknowledges, as it did in its Post-Hearing Comments, that
once the coke oven gas desulfurization unit is in operation, there is a possibility that the
emissions limitation may require adjustment, which would be the subject of a future
rulemaking.” PC 22 at 2;
see
PC 11 at 23.
Third, the Agency notes that U.S. Steel has requested that the Board revise “the proposed
testing and monitoring provisions under Section 217.157 in order to be consistent with its
construction permit for its cogeneration boiler with a heat input capacity” of 505 mmBtu/hr. PC

25
22 at 2. The Agency states that the permit requires installation and operation of a NO
x
and CO
CEMS “within one year after the initial emission testing required by the permit unless this
testing or further testing demonstrates that the unit normally complies by a margin of at least 5
percent with the NO
x
and CO emission limit in the permit or the Illinois EPA approves further
time for U.S. Steel to achieve this level of performance.”
Id
. The Agency further states that the
proposed Section 217.157(a)(1) “requires the installation and operation of a CEMS on industrial
boilers with a rated heat input capacity greater than 250 mmBtu/hr.”
Id
.
The Agency reports that, after additional discussion with U.S. Steel, it recommends
amending the proposed Section 217.157(a)(1) to read as follows:
[t]he owner or operator of an industrial boiler subject to Subpart E of this Part
with a rated heat input capacity greater than 250 mmBtu/hr must install, calibrate,
maintain, and operate a continuous emissions monitoring system on the emission
unit for the measurement of NO
x
emissions discharged into the atmosphere in
accordance with 40 CFR Part 75, as incorporated by reference in Section 217.104.
However, the owner or operator of an industrial boiler subject to Subpart E of this
Part with a rated heat input capacity greater than 250 mmBtulhr that combusts
blast furnace gas with up to 10% natural gas on an annual basis and located at a
source that manufactures iron and steel is not required to install, calibrate,
maintain, and operate a continuous emissions monitoring system on such
industrial boiler, provided the heat input from natural gas does not exceed 10% on
an annual basis and the owner or operator complies with the performance test
requirements under this Section and demonstrates, during each performance test,
that NO
x
emissions from such industrial boiler are less than 70% of the applicable
emissions limitation under Section 217.164. In the event such owner or operator
is unable to meet the requirements of this paragraph, a continuous emissions
monitoring system is required within 12 months of such event, or by December
31, 2012, whichever is later. PC 22 at 3.
Fourth, the Agency states that it agrees with U.S. Steel that the denominator in the
equation in the proposed Section 217.164(e) needs correction. PC 22 at 3. The Agency notes
that its own first notice comments proposed the same correction.
Id
.;
see
PC 17 at 4.
ArcelorMittal
While the Agency notes that ArcelorMittal has restated its position that the proposed NO
x
emissions limitation for reheat furnaces is economically unreasonable, the Agency states the
belief that “the proposed limitation for reheat furnaces (recuperative, combusting natural gas) is
technically feasible and economically reasonable, and that the information contained in the
docket for this rulemaking adequately supports the proposed limitation.” PC 22 at 3-4.
Accordingly, the Agency now opposes any revision of that limitation.
Id.
at 3.
The Agency also notes that ArcelorMittal has renewed its request that the proposal
“provide an option for a case-by-case exemption of the NO
x
emissions limitation upon a
demonstration that such controls would be economically unreasonable.” PC 22 at 4. The

26
Agency states that it opposes such an option.
Id
. The Agency argues that Board regulations
include mechanisms for regulatory relief.
Id
. The Agency indicates that it “is willing to work
with affected sources, including ArcelorMittal, that may seek relief from unreasonable impacts
due to unique or source-specific circumstances.”
Id
.
FIRST NOTICE ISSUES
In both the first and second motions to amend its rulemaking proposal, the Agency
indicates that it has negotiated with interested participants and agreed to revise certain provisions
in order to memorialize agreements with them.
See generally
Mot. Amend 1 at 1-2, Mot. Amend
2 at 1-5. In its first notice comments, the Agency proposed additional corrections to and
clarifications of its proposal. PC 17 at 1-6. These various amendments address many of the
issues raised by the participants over the course of the rulemaking process. However, first notice
comments demonstrate that the participants have not reached agreement on all issues. The Board
will briefly discuss the unresolved issues in the following subsections. The Board then provides
a detailed section-by-section discussion of the proposed rules following the Board’s findings on
economic reasonableness and technical feasibility.
ArcelorMittal
ArcelorMittal’s first notice comment clarifies that ArcelorMittal has not reached an
agreement with the Agency regarding the proposed emission limit for recuperative reheat furnace
and asserts that the proposed limit is not supported by technical or economic justification. PC 15
at 2. ArcelorMittal contends that it has also successfully demonstrated in its previous comments
that the initial NO
x
emission limit proposed by the Agency was arbitrary, technologically
infeasible, and economically unreasonable. ArcelorMittal requests that the Board “reconsider
the proposed revised arbitrary emission limit (0.09 lb/mmbtu) requested by the Agency based on
the economic reasonableness, technical feasibility and product quality issues.”
Id.
In the
following sections, the Board will provide a brief background concerning the proposed NO
x
emission limit; ArcelorMittal’s and the Agency’ positions concerning the emission limit for
reheat furnaces; and the Board’s discussion and finding.
Background
The Agency’s initial proposal included a NO
x
emissions limit of 0.05 lb/mmBtu for
recuperative reheat furnaces used in iron and steel making. Prop. at 50 (proposed Section
217.244(a)(2)). In comments filed on November 25, 2008, ArcelorMittal raised concerns
regarding the applicability of the proposed emissions limitation to a tunnel furnace at its
Riverdale Facility. ArcelorMittal stated that the proposed limitation is inappropriate for its
tunnel furnace there because it cannot be considered as a reheat, annealing, or galvanizing
furnace. Further, ArcelorMittal argued that, even if the Agency considers the tunnel furnace to
be subject to the proposed regulations, the rules should include a specific definition and emission
factor for ArcelorMittal’s tunnel furnace. ArcelorMittal Comment at 1.
In post-hearing comments, ArcelorMittal reiterated its initial concerns regarding the
proposed emissions limitations for reheat furnaces. Additionally, ArcelorMittal argued that

27
setting and implementing additional NO
x
controls is neither technologically feasible nor
economically reasonable. PC 10 at 1, 2.
For the February 3, 2009 hearing, the Agency testified that it was working with
ArcelorMittal regarding the emissions limitation for reheat furnaces. Kaleel Prefiled Test. 2 at 2.
On March 23, 2009, the Board received the Agency’s second motion to amend its proposal. In
that motion, the Agency proposed to amend the NO
x
emissions limit for recuperative reheat
furnaces from 0.05 lb/mmBtu to 0.09 lb/mmBtu. The Agency stated that, “[s]ince the last
hearing, the Illinois EPA has continued to engage in negotiations with interested parties on
remaining unresolved issues.” Mot. Amend 2 at 1. The Agency further stated that such
negotiations with ConocoPhillips, U.S. Steel, and ArcelorMittal have resulted in agreement to
amend various provisions of the proposal.
Id.
at 1-2. The Board adopted the revised emissions
limit for recuperative reheat furnace for first notice. In the Matter of: Nitrogen Oxides
Emissions from Various Source Categories: Amendments to 35 Ill. Adm. Code Parts 211 and
217, R08-19, slip op. at 104 (May 7, 2009) (proposed Section 217.244(a)(2)).
Proposed First Notice Emission Limit
ArcelorMittal claims that, when the Agency revised its proposed NO
x
emission limit for
reheat furnaces to 0.09 lb/mmBtu, the Agency failed to provide any further technical or
economical justification and also failed to demonstrate that the revised limit was based on
RACT. PC 15 at 2. However, ArcelorMittal notes that it did receive information
2
relied upon by
the Agency in establishing the revised limit and that the first notice comments are based on a
review of that information.
ArcelorMittal notes that the emission limit of 0.0147lb/mmBtu listed for the reheat
furnace at Beta Steel in the Agency’s summary table has been changed in that furnace’s permit to
0.077 lb/mmBtu. PC 15 at 3;
see
PC 20 at 2 n.1 (correcting original reference to limit of 0.77
lb/mmBtu). ArcelorMittal maintains that two other facilities, Nucor Steel and V & M Star, are
not similar to ArcelorMittal’s Riverdale facility. PC 15 at 3. ArcelorMittal continues that the
emission limits listed for New Steel International and Minnesota Steel Industries are for facilities
that are yet to be constructed.
Id.
at 4. Lastly, ArcelorMittal states that, while the Severstal
Columbus facility is similar to the Riverdale facility, the Severstal facility has two tunnel
furnaces, which can have an effect on the applicable emission limit. ArcelorMittal notes that,
since the Riverdale facility does not have a second tunnel furnace or a shuttle furnace, it does not
have the flexibility to operate optimally at all times if required to retrofit the tunnel furnace with
new burners.
Id.
at 5-6. Moreover, ArcelorMittal notes that the Severstal facility has not been
issued a Title V permit. Therefore, ArcelorMittal claims that “achievement of the emissions
limit for these facilities have not been demonstrated.”
Id.
at 4. ArcelorMittal maintains that the
Agency’s “arbitrary determination that 0.09 lb/mmBtu is technically feasible and the appropriate
RACT-based limit for reheat furnaces” is questionable.
Id.
2
The information attached to ArcelorMittal’s comments as Exhibit A consists of a summary
table of permitted NO
x
emissions levels for tunnel furnaces at seven steel plants.

28
ArcelorMittal maintains that the revised emission limit does not alter its earlier position
concerning the economic reasonableness of the initial emission limit. ArcelorMittal states that
the revised emission limit of 0.09 lb/mm Btu does not change the earlier cost analysis because
ArcelorMittal would still have to install one of the two next generation burners to meet the
revised emission limit. PC 15 at 5. ArcelorMittal argues that spending more than $22,000 per
ton of NO
x
controlled is economically unreasonable for a point source that contributes
approximately 0.016 percent of the total 2006 Chicago area daily NO
x
inventory of 812 tons.
Id.
In addition, ArcelorMittal states that changing burners on the tunnel furnace can have significant
effect on the slab quality. Also, ArcelorMittal states that the unique product mix produced at the
Riverdale facility differentiates ArcelorMittal’s facility from other steel making facilities
throughout the country. ArcelorMittal concludes by requesting that the Board “revisit its
Proposed Rule and for Second Notice allow a source to be exempt from the proposed NO
x
emission limits upon adequate demonstration that additional NO
x
controls would be
economically unreasonable.”
Id.
at 6-7. ArcelorMittal maintains that it has made such a
demonstration and requests that the tunnel furnace at the Riverdale be subject to its currently
applicable permitted emission limit in lieu of the proposed emission limit for reheat furnaces.
Id.
at 7.
Agency Response
The Agency responds to ArcelorMittal by noting that the information in the TSD
indicates that the NO
x
control technologies identified for reheat, annealing, and galvanizing
furnaces at iron and steel plants are reasonably available, technically feasible, and cost effective,
even considering the tunnel design of ArcelorMittal’s reheat furnace. PC 17 at 7. The Agency
also addresses the issues raised by ArcelorMittal concerning the NO
x
limitations for reheat
furnaces at other sources listed in the Agency’s summary table. The Agency notes that the
emission limit for Beta Steel in Indiana is actually 0.077 lb/mmBtu, which is more stringent than
the proposed emission limit. Additionally, the Agency states that the emission limits in the
construction permits of plants that have not yet been constructed are enforceable limits. The
Agency argues that the emission limits in the summary table support the proposed limit as
technologically feasible.
Id.
at 8.
Additionally, the Agency raises concerns regarding ArcelorMittal’s economic analysis,
claiming that it is flawed and should not be considered for making a determination that the
proposed limit is beyond RACT. First, the Agency states that the burners currently in use at the
Riverdale facility were designed in the 1980s and are not considered an “advanced NO
x
control
technology”.
Id.
Next, the Agency notes that ArcelorMittal’s estimates of the cost effectiveness
are based on assumptions that overstate the annualized costs. The calculation assumes an
equipment life of only 5 years, which the Agency claims is unreasonable considering that the
existing burners are about 20 years old.
Id.
The Agency also states that the interest rate of 10
percent and the contingency factor of 20 percent are high.
The Agency further states that ArcelorMittal requests a case-by-case RACT analysis,
which is not provided for in the proposal. Further, the Agency states that it opposes inclusion of
such options in the proposed rules.
Id.
at 9. The Agency notes that the Board regulations

29
include mechanisms for regulatory relief that sources may use under certain circumstances to
seek relief from the rules of general applicability.
ArcelorMittal Response
On July 7, 2009, ArcelorMittal submitted a response to address concerns raised by the
Agency concerning the emission limit for reheat furnaces. ArcelorMittal asserts that the five-
year equipment life and a contingency factor of 20 percent are based on USEPA published
values. PC 20 at 1. The equipment life factor is derived from USEPA’s “Alternative Control
Technique Document – NO
x
Emissions from Iron and Steel Mills,” EPA/453/R-94-065,
September 1994, and the contingency factor is derived from USEPA’s “Cost Air” spreadsheets
available online at www.epa.gov/ttn.
Id.
at 1-2. However, to address the Agency’s concerns,
ArcelorMittal states that it prepared a revised economic analysis for burner change using a 15-
year equipment life and a contingency factor of 10 percent. The revised analysis estimates a cost
effectiveness of $10,348 per ton of NO
x
reduced for the next generation 1500 burner and a cost
effectiveness of $17,841 per ton of NO
x
reduced for the 1550 burner. These costs, ArcelorMittal
contends, are well in excess of the Agency’s established range of $2500-3000 per ton of NOx
emission reduction, USEPA’s determination of less than $2,000 per ton, and the reference in the
TSD to $1,000 per ton.
Id.
at 2.
Regarding the emission limits of other reheat furnaces, ArcelorMittal acknowledges that
it inadvertently cited to Beta Steel’s emission limit as 0.77 lb/mmBtu instead of 0.077 lb/mmBtu.
However, ArcelorMittal notes that the Agency had listed Beta Steel’s emission limit as 0.0147
lb/mmBtu, which is approximately five times lower than the permitted limit.
Id.
ArcelorMittal
argues that the Agency’s reliance on Beta Steel’s emission limit calls into question the arbitrary
limit proposed by the Agency. ArcelorMittal maintains that the Agency has failed to
demonstrate that its proposal is both economically reasonable and technically feasible.
Id.
at 3.
Therefore, ArcelorMittal requests that the Board make a decision based on RACT and retain the
current permitted emission limit of 0.171 lb/mmBtu for ArcelorMittal’s tunnel furnace at its
Riverdale facility, and not require ArcelorMittal to initiate a proceeding for subsequent
regulatory relief.
Id.
Discussion
The Board’s first notice proposal at Section 217.244(a)(2) sets forth a revised emissions
limit of 0.09 lb/mmBtu for recuperative reheat furnaces combusting natural gas. The Board
adopted the revised emission limit for first notice based on the Agency’s expert testimony,
comments, and information in the TSD. While ArcelorMittal had raised concerns about the
initial emission limit of 0.05 lb/mmBtu, the Board believed that the revised limit proposed in the
Agency’s second motion to amend addressed ArcelorMittal’s concerns, particularly since
ArcelorMittal did not respond to the second motion to amend. However, since ArcelorMittal has
reiterated its concerns regarding the proposed emission limit for reheat furnaces in its first notice
comments, the Board will examine the issues raised by ArcelorMittal regarding the application
of the proposed NO
x
emissions limit for recuperative reheat furnaces to ArcelorMittal’s tunnel
furnace.

30
ArcelorMittal questions the technical feasibility and economic reasonableness of the
proposed reheat furnace emission limit, which, according to the Agency, is based on a survey of
the NO
x
emission limits for furnaces similar to ArcelorMittal’s tunnel furnace. The Agency’s
survey, which was submitted by ArcelorMittal as an exhibit to its first notice comments, includes
NO
x
emission limit information for reheat tunnel furnaces at seven steel plants. See PC 15,
Exhibit A. The NO
x
emission limits for the plants included in the Agency’s survey range from
0.03 lb/mmBtu to 0.10 lb/mmBtu.
ArcelorMittal argues that the Agency relies on outdated, erroneous or never applied in
practice emission limits to support the proposed reheat furnace emission limit. PC 15 at 4. First,
ArcelorMittal notes that two of the facilities in the Agency’s survey, Nucor Steel and V&M Star,
are not similar to its Riverdale facility. ArcelorMittal states that Nucor Steel has an equalizing
furnace and V&M Star has a billet furnace, both of which are different from ArcelorMittal’s
tunnel furnace.
Id.
at 5-6. However, ArcelorMittal does not explain how these differences
among these furnaces affect the appropriate NO
x
emission limitations for them. While the Board
believes that ArcelorMittal may have raised a valid concern regarding the differences between
the furnaces, the Board cannot draw any conclusions without additional information concerning
the impact of those differences on the control of NO
x
emissions.
Second, ArcelorMittal contends that emission limits from Minnesota Steel and New Steel
International are not relevant since the plants have yet to be constructed. In this regard, the
Board agrees with the Agency that emission limits in a construction permit are enforceable limits
that provide support for the technical feasibility of the proposed emission limit. Next,
ArcelorMittal notes that, although the Severstal Columbus plant is similar to the Riverdale
facility, the Severstal plant’s two tunnel furnaces can affect the applicable emission limits.
ArcelorMittal notes that lack of redundancy in the operation at the Riverdale facility limits
ArcelorMittal’s ability to divert product between furnaces. While the Board recognizes that
having only one tunnel furnace limits operational flexibility, ArcelorMittal’s comments do not
clearly explain why such flexibility is necessary to achieve the proposed emission limit.
Finally, the Board notes that ArcelorMittal does not address the remaining two steel
plants in the Agency survey,
i.e
., Beta Steel and Gallatin Steel. These plants have permitted
emission limits in the same range as the proposed emissions limit of 0.09 lb/mmBtu. Based on
the information in the Agency’s survey, the Board finds that the proposed NO
x
emissions limit of
0.09 lb/mmBtu is technically feasible for recuperative reheat furnaces, including tunnel furnaces.
While ArcelorMittal has raised some concerns regarding the information considered by the
Agency as it applies to its Riverdale facility, those concerns do not rise to a level at which the
Board needs to reconsider its decision at first notice. Also, the Board believes that some of the
issues raised by ArcelorMittal must be developed further before the Board can consider a site-
specific RACT determination for the Riverdale facility.
Regarding the compliance costs, ArcelorMittal argues that the proposed emissions limit
for reheat furnaces is economically unreasonable. As noted above, ArcelorMittal revised its
economic analysis in response to Agency comments. The revised analysis estimates the cost
effectiveness based on the replacement of the tunnel furnace’s existing burner with two different
models using a 15-year equipment life and a 10 percent contingency factor. PC 20 at 2. The

31
revised estimates of cost effectiveness are $10,348 per ton of NO
x
reduced for a “1500 series
burner” and $17,841 per ton of NO
x
reduced for a “1550 series burner.” ArcelorMittal argues
that the revised site-specific estimates of cost effectiveness for the Riverdale facility are higher
than the Agency’s estimate of $3000 per ton of NO
x
reduced.
While ArcelorMittal’s estimate of cost effectiveness for NO
x
control at its Riverdale
facility is higher than the Agency’s estimate, the Board notes that the Agency’s estimate is based
on generic cost data from the federal Alternative Control Technique documents for iron and steel
plants. TSD at 98-99. The Board relied on the Agency’s estimate of cost effectiveness in
finding the proposed generally applicable NO
x
emissions limit for reheat furnaces to be
economically reasonable. The Board recognizes that compliance costs may be higher or lower
than the Agency’s estimate of $3000 per ton of NO
x
reduced depending on site-specific factors,
but the Board is not adopting an emission limit based on site-specific factors in this rulemaking.
The Board notes that the economic information presented by the Agency in the TSD supports the
Board finding that the proposed emissions limit is economically reasonable. While
ArcelorMittal has raised concerns regarding the technical feasibility and economic
reasonableness of applying the proposed reheat furnace emission limit to the Riverdale facility’s
tunnel furnace, the Board believes that the record is insufficient to support the adoption of a site-
specific emissions limit in this proceeding.
Specifically, the Board believes that ArcelorMittal must fully address some of the
technical issues relating to its claim that emission limits listed in the Agency’s survey are not
applicable to ArcelorMittal’s tunnel furnace. In addition, ArcelorMittal must address Agency’s
contention that the Series 1430 burners now in use at the Riverdale facility were designed in the
1980s and are not considered an “advanced NO
x
control technology.” PC 17 at 8. Finally, even
if the Board accepts ArcelorMittal’s position that the proposed NO
x
emission limit for reheat
furnaces is economically unreasonable for the Riverdale Facility, the record lacks sufficient
information other than ArcelorMittal’s assertions on which the Board can rely to determine that
the current permitted emission limit of 0.171 lb/mmBtu is RACT for the tunnel furnace at the
Riverdale facility.
In light of these factors, the Board declines to adopt a site-specific NO
x
emissions limit
for the Riverdale facility in this rulemaking proceeding. However, as noted by the Agency in its
response filed July 15, 2009, the Act and the Board’s regulations include regulatory relief
mechanisms through which ArcelorMittal may address these matters in support of the
determination it seeks.
See, e.g.
, 415 ILCS 5/27, 28, 28.1 (2008); 35 Ill. Adm. Code 102.208,
102.210, 104.Subpart D (addressing site-specific rulemaking and adjusted standards). The Board
notes that Section 28.1(f) of the Act provides in pertinent part that,
[w]ithin 20 days after the effective date of any regulation that implements in
whole or in part the requirements of the Clean Air Act, if any person files a
petition for an individual adjusted standard in lieu of complying with the
regulation, such source will be exempt from the regulation until the Board makes
a final determination on the petition. 415 ILCS 5/28.1(f) (2008).
IERG

32
Averaging Provisions
Section 217.158(a)(1)(C).
IERG’s comment states that it “is substantially in agreement
with the Board’s determination to revise the language of Section 217.158(a)(1)(C), regarding the
inclusion of ‘replacement units’ in emission averaging plans, as suggested by both IERG and the
Agency.” PC 16 at 5. However, IERG proposes that the Board insert a comma at a specified
point in the subsection “for the purpose of clarity.”
Id
. Having reviewed IERG’s comment and
the proposed Section 217.158(a)(1)(C), the Board cannot conclude that the addition of a comma
would provide clarification and declines to adopt this proposed amendment.
Section 217.158(d)(1).
IERG suggests that proposed Section 217.158(d)(1) be struck as
“unnecessary.” PC 16 at 6. As an alternative, IERG suggests that, if it retains subsection (d)(1)
for recordkeeping purposes, the Board revise it so that an amended averaging plan is required
only in the event that a unit listed in the plan is “permanently shut down.”
Id
. at 6-7.
IERG contemplates that the Board may conclude that subsection (d)(1) fulfills
recordkeeping purposes.
See
PC 16 at 6. The record does not demonstrate that it is unnecessary
for or inconsistent with those purposes, and the Board declines at this point in the proceedings to
strike it from the proposed rules. The Board notes that IERG proposes alternative language for
this subsection in the event that the Board declines to strike it.
Id
. IERG suggests that replacing
the phrase “taken out of service” with “permanently shut down” would make this subsection
clearer. After reviewing IERG’s comment and the record, the Board cannot conclude that the
proposed alternative language improves the clarity of this provision. In addition, the Board notes
that IERG has proposed changing from 30 to 90 days that amount of time in which an owner or
operator must submit an amended plan after taking a unit out of service.
Id
. As IERG’s first
notice comment includes no argument that the 30-day period is insufficient, the Board declines
to adopt the changes to Section 217.158(d)(1).
Section 217.158(d)(2).
IERG notes that proposed Section 217.158(d)(2) “allows units
that were previously exempt to be included in an averaging plan ‘within 30 days after the unit no
longer qualifies for the exemption.’” PC 16 at 7. IERG suggests that this 30-day limit is not
necessary, as a unit becomes subject to all applicable provisions of the proposed rule once it is no
longer exempt.
Id
. IERG further suggests that the provision does not clearly indicate whether,
after that 30-day period, the owner or operator is no longer able to include the unit in an
averaging plan if then plan is not updated during that time.
Id
. IERG proposes that Section
217.158(d)(2) be amended to allow the owner or operator to amend its existing averaging plan
“at any time” to include a unit that is no longer exempt. IERG claims that this amendment is
consistent with the Agency’s intent in providing exceptions to the limit of one amendment per
calendar year to an emissions averaging plan.
Id
.
The Board notes that the proposed subsection (d)(2) allows an owner or operator to
include a unit that was exempt from specified requirements in an emissions averaging plan
“within 30 days after the unit no longer qualifies for an exemption.” In addition, the proposed
subsection (c) provides that an owner or operator may amend an emissions averaging plan once
per year at their own discretion.
See
MG Answers at 4. Responding to a question posed for the

33
first hearing by Midwest Generation, the Agency stated that it did not intend “to establish a ‘once
out/always out’ provision.”
Id
. Specifically, the Agency stated that, through the allowed annual
revisions, a unit not originally included in an averaging plan may later be included in such a
plan.
See id
. Considering both the proposed language of Section 217.158 and the Agency’s
statement of intent, the Board concludes that, if a unit no longer qualifies for an exemption, the
owner or operator may include that unit in an averaging plan once within 30 days after the unit
no longer qualifies for an exemption and again on an annual basis thereafter. Accordingly, the
Board declines to adopt the language proposed by IERG.
Section 217.158(h).
IERG states that “proposed [S]ection 217.158(h) would allow
exclusion from the ‘calculation demonstrating compliance’ certain time periods when a unit is
shut down for a maintenance turnaround.” PC 16 at 7. IERG notes that, in order to avail itself of
this proposed exemption, the owner or operator must first notify the Agency in writing in
advance. IERG requests that the Board clarify this subsection to provide that, while the period
excluded from the calculation must not exceed 45 days, the actual maintenance turnaround is not
limited to a 45-day duration.
Id
. IERG proposes specific language to effectuate this intent.
Id
.
The Board notes that proposed subsection (h) allows the owner or operator of a unit
located at a petroleum refinery to “exclude from the calculation demonstrating compliance”
periods of up to 45 days during which the unit is shut down a maintenance turnaround after
providing notice to the Agency. While the Board notes IERG’s comment that the maintenance
turnaround itself may last longer than 45 days, the Board concludes that the proposed subsection
limits to 45 days the period that may be excluded from the calculation demonstrating
compliance. The Board cannot conclude that the language requires the maintenance actually to
be performed with that 45-day period and declines to adopt the proposed revision.
Types of Units Not in Nonattainment Areas
IERG restates its position that the proposed rules should not establish emissions limits for
types of units that are not now located in the nonattainment areas. PC 16 at 8 (citations omitted).
IERG acknowledges that the Agency has not concurred with the request to omit emissions limits
for these units.
Id
. at 9.
IERG argues that it establishes “inappropriate and, even perhaps, troublesome”
precedents to establish emission limits for these units. PC 16 at 9. IERG claims that analyses of
specific units that may operate in the nonattainment areas could demonstrate that the proposed
emissions limits are not RACT for a particular unit.
Id
. IERG argues that the opportunity to
perform analyses of this kind would effectively pass with the adoption of this proposed rule.
Id
.
IERG also expresses concern that the proposed emission limits may be viewed as the “RACT
floor” for units located outside of nonattainment areas.
Id
. IERG argues that owners and
operators of such units have not had cause or opportunity to participate in this rulemaking and
that they may have difficulty complying with the proposed limits.
Id
. at 9-10.
Addressing limits for these types of units, the Agency states that it has performed the
engineering and cost analysis on which the limits are based. Tr.1 at 62;
see
TSD at 66-85, 118-
25. The Agency argues that the proposed rule would guide those units if nonattainment areas

34
expand through a rulemaking to include them. Tr.1 at 62. The Agency also argues that,
although new source standards are generally more stringent than RACT, new source applicants
frequently seek alternatives to those standards. PC 11 at 20. The Agency claims that emission
units may seek to operate in the nonattainment areas and that it is reasonable that new sources
there should at a minimum meet RACT requirements. PC 11 at 20. The Agency further claims
that the proposed standards “will provide a floor for future emission sources that may seek to
locate in these areas.”
Id
.
Addressing emissions limits in its first notice comment, IERG acknowledges that
benchmarks have some value. PC 16 at 4. IERG also expresses general agreement that new
sources should theoretically be subject to emissions requirements more strict than a RACT rule.
Id
. The Board agrees with the Agency’s general position that the proposed emission standards
serve as benchmark for future emission sources that may locate in the nonattainment areas and
provide a “floor” against which to compare the new source standards. The Board notes IERG’s
argument that a site-specific analysis of the controls constituting BACT or LAER for a new
source could conceivably generate a less stringent emissions limitation than RACT. However,
the Board cannot conclude that this possibility outweighs the value of establishing a benchmark.
The Board also notes IERG’s concern with the potential application of the proposed
emissions limits “to units outside of the nonattainment areas covered by the proposed rule.” PC
16 at 10. In this regard, the Board notes that the applicability provision at Section 217.150 of the
proposed rule explicitly identifies the geographical extent of the nonattainment areas. The
Agency has clearly testified that any designation of a new nonattainment area would require the
Agency to propose an amendment to the rule. Tr.1 at 57, 61. The Board conceives that such a
rulemaking proceeding may address emissions limits in addition to the geographical boundaries
of the nonattainment area.
After careful review of the rule proposed at first notice and IERG’s comments, the Board
declines to strike from the proposal emissions limits for types of units not now in the
nonattainment areas.
Reporting Requirements
IERG notes Section 217.156(j)(1) and (j)(2) regarding quarterly reports from owners or
operators of units demonstrating compliance through CEMS. IERG first proposed to delete
subsection (j)(1) on reporting CEMS down time because it refers to information contained in the
provisions of the Code of Federal Regulations that are cited in subsection (j)(2). PC 16 at 11.
In subsection (j)(2), IERG proposes to strike a reference to 40 C.F.R. 60.13, arguing that
it pertains to monitoring and not to the recordkeeping and reporting that are the subjects of this
section. IERG also proposes to amend the reference to 40 C.F.R. 75 by citing specifically to 40
C.F.R 75.73(f). IERG argues that this amended citation refers specifically to quarterly reporting
requirements. IERG further argues that Section 217.157 addressing testing and monitoring refers
to the general CEMS requirements under Part 75.

35
Having reviewed the proposed subsection (j) and the provisions of the Code of Federal
Regulations cited in it, the Board cannot conclude that subsection (j)(1) is entirely embodied
within subsection (j)(2) or that the two subsections conflict with one another. Accordingly, the
Board declines to strike subsection (j)(1). In subsection (j)(2), the Board declines to add
language referring specifically to a “summary report,” which is specifically addressed in the
cited provisions of the Code of Federal Regulations.
See
40 C.F.R. 60.7(c), (d). Also, having
reviewed the language of 40 C.F.R. 60.13, the Board cannot conclude that it is unrelated to the
recordkeeping and reporting provisions of the proposed Section 217.156 and declines to strike
the reference to it. Finally, while noting IERG’s comment that 40 C.F.R. 75.73(f) specifically
addresses quarterly reports, the Board after examining Part 75 cannot conclude that only Section
75.73(f) may be relevant to those reports under proposed Section 217.156(j). Accordingly, the
Board declines to amend that citation as proposed by IERG.
Argonne
Performance Testing
In its comment dated July 6, 2009, Argonne states that the proposed Section 217.154(a)
“requires performance testing for all industrial boilers regardless of size, unless they employ
CEMS.” PC 21 at 1. Argonne further states that, under the proposed Section 217.166, industrial
boilers with a rated heat input less than or equal to 100 mmBtu/hr are required to perform
combustion tuning instead of complying with a numeric NO
x
emissions limitation.
Id
. Argonne
proposes, for industrial boilers with such a rated capacity, “that performance testing not be
required.”
Id
.
In its comment filed on July 6, 2009, the Agency clarified Section 217.154(a) to refer to
performance testing for units subject to “emissions limitations” under the proposed Subparts E,
F, G, H, or I . PC 17 at 2-3. The Agency also sought to add an exclusion from the performance
testing requirement for units demonstrating compliance through alternatives including
combustion tuning.
Id
. While Argonne’s and the Agency’s comments do not refer to one
another, the Board concludes that the Agency’s clarification addresses Argonne’s proposal.
In its comment, Argonne states that, “[f]or boilers less than or equal to 100 mmBtu/hr
rated heat input demonstrating compliance through an emission averaging plan and not using
CEMS, Section 217.157(a)(4) requires performance testing. . . .” PC 21 at 1. Argonne argues,
however, that the subsection “does not address boilers less than or equal to 100 mmBtu/hr rated
heat input where emissions averaging is not used.”
Id
. While the proposed Section
217.157(a)(4) does not specifically refer to industrial boilers with such a rated capacity that are
not part of an emission averaging plan, it does not require that they undergo an initial
performance test. These different requirements, based on whether boilers are or are not part of
an averaging plan, are generally consistent with the clarification described in the preceding
paragraph. Consequently, the Board cannot conclude that the proposed Section 217.157(a)(4)
requires amendment.
CEMS/PEMS

36
Argonne argues that the use of CEMS should not be required for industrial boilers with a
rated heat input less than or equal to 100 mmBtu/hr that are required to perform combustion
tuning instead of complying with a numeric NO
x
emissions limitation. PC 21 at 1. Argonne
generally argues that, since those units are not required to comply with a numeric NO
x
emissions
limit, the use of CEMS or PEMS appears to be unnecessary.
Id
. Nonetheless, Argonne states
that CEMS or PEMS “could be employed at the option of the facility” if, for example, it opts to
rely on emissions averaging to demonstrate compliance.
Id
.
Under the proposed Section 217.157(a)(5), the owner or operator of an industrial boiler
with a rated heat input capacity less than or equal to 100 mmBtu/hr demonstrating compliance
through an emission averaging plan
may
, instead of conducting an initial performance test under
subsection (a)(4), install and operate CEMS.
See
In the Matter of: Nitrogen Oxides Emissions
from Various Source Categories: Amendments to 35 Ill. Adm. Code Parts 211 and 217, R08-19,
slip op. at 88 (May 7, 2009) (proposed Section 217.157(a)(5)) (emphasis added). If an owner or
operator opts to rely upon CEMS, it “must” use the system to demonstrate compliance with the
applicable emissions averaging plan.
Id
.
While Argonne’s comment suggests that a boiler might use CEMS “in place of emissions
averaging,” operating CEMS is not itself a compliance option.
See
PC 21 at 1. Under proposed
Section 217.157(a)(5), CEMS is an alternative to performance testing in demonstrating
compliance with an emissions averaging plan. Consequently, the Board concludes that the
proposed language is generally consistent with Argonne’s comments and declines to amend
Section 217.157(a)(5). On similar grounds, the Board also declines to amend Section 217.157(f),
which provides the owner or operator of specified units “may” rely on PEMS.
See
In the Matter
of: Nitrogen Oxides Emissions from Various Source Categories: Amendments to 35 Ill. Adm.
Code Parts 211 and 217, R08-19, slip op. at 91 (May 7, 2009).
ECONOMIC REASONABLENESS AND TECHNICAL FEASIBILITY
The Board notes that the Agency has negotiated with interested participants and agreed to
revise certain provisions in order to memorialize agreements with them.
See generally
Mot.
Amend 1 at 1-2, Mot. Amend 2 at 1-5. The Agency has more recently proposed additional
clarifications of and corrections to its proposal. PC 17 at 1-6. These amendments have
addressed issues including, but not limited to, compliance deadlines, deadlines for installing
CEMS, and emissions limitations.
Id
. Having granted the Agency’s two motions to amend the
proposal and adopting additional clarifications and corrections, and having reviewed the entire
record in this proceeding, the Board finds that its second notice proposal is technologically
feasible and economically reasonable.
The Board proceeds below with its section-by-section discussion of its second notice
proposal.
SUMMARY OF BOARD’S SECOND NOTICE PROPOSAL
Part 211: Definitions and General Provisions

37
The Board proposes to add twelve new definitions to the existing Part 211. Statement at
13;
see
Prop. at 13-15;
see generally
35 Ill. Adm. Code 211. The Board summarizes each of the
proposed new definitions below.
Section 211.665: Auxiliary Boiler
In its proposal, the Agency sought to add a definition of the term “auxiliary boiler,”
which is necessitated by the proposed Subparts D and E. Statement at 14. In its entirety, the
proposed definition states that “‘[a]uxiliary boiler’ means, for the purpose of Part 217, a boiler
that is operated only when the main boiler or boilers at a source are not in service and is used
either to maintain building heat or to assist in the startup of the main boiler or boilers. This term
does not include emergency or standby units and load shaving units.” Prop. at 13 (proposed new
Section 211.665).
Section 211.995: Circulating Fluidized Bed Combustor
In its proposal, the Agency sought to add a definition of the term “circulating fluidized
bed combustor,” which is necessitated by the proposed Subpart E. Statement at 14. In its
entirety, the proposed definition states that “‘[c]irculating fluidized bed combustor’ means, for
purposes of Part 217, a fluidized bed combustor in which the majority of the fluidized bed
material is carried out of the primary combustion zone and is transported back to the primary
zone through a recirculation loop.” Prop. at 14 (proposed new Section 211.995).
Section 211.1315: Combustion Tuning
In its proposal, the Agency sought to add a definition of the term “combustion tuning,”
which is necessitated by Subparts E and F. Statement at 14. In its entirety, the proposed
definition states that “‘[c]ombustion tuning’ means, for purposes of Subpart 217, review and
adjustment of a combustion process to maintain combustion efficiency of an emission unit, as
performed in accordance with procedures provided by the manufacturer or by a trained
technician.” Prop. at 14 (proposed new Section 211.1315).
Section 211.1435: Container Glass
In its proposal the Agency sought to add a definition of the term “container glass,” which
is necessitated by Subpart G. Statement at 14. In its entirety, the proposed definition states that
“‘[c]ontainer glass’ means, for purposes of Part 217, glass made of soda-lime recipe, clear or
colored, which is pressed or blown, or both, into bottles, jars, ampoules, and other products listed
in Standard Industrial Classification 3221.” Prop. at 14 (proposed new Section 211.1435).
Section 211.2355: Flare
In its proposal, the Agency sought to add a definition of the term “flare.” Prop. at 14.
The Agency stated that the proposed definition is necessary “because flares are not subject to the
NO
x
general requirements under Subpart C.”
Id
. In its entirety, the proposed definition states

38
that “‘[f]lare’ means an open combustor without enclosure or shroud.” Prop. at 14 (proposed
new Section 211.2355).
Section 211.2357: Flat Glass
In its proposal, the Agency sought to add a definition of the term “flat glass,” which is
necessitated by Subpart G. Statement at 14. In its entirety, the proposed definition states that
“‘[f]lat glass’ means, for purposes of Part 217, glass made of soda-lime recipe and produced into
continuous flat sheets and other products listed in Standard Industrial Classification 3211.”
Prop. at 14 (proposed new Section 211.2357).
Section 211.2625: Glass Melting Furnace
In its proposal, the Agency sought to add a definition of the term “glass melting furnace,”
which is necessary for applicability under Subpart G. Statement at 14. In its entirety, the
proposed definition states that “‘[g]lass melting furnace’ means, for purposes of Part 217, a unit
comprising a refractory vessel in which raw materials are charged, melted at high temperature,
refined and conditioned to produce molten glass.” Prop. at 14-15 (proposed new Section
211.2625).
In its pre-hearing comment filed January 20, 2009, Saint-Gobain suggested amending this
proposed definition to state that “‘[g]lass melting furnace’ means, for purposes of Part 217, a unit
comprising a refractory vessel in which raw materials are charged and melted at high
temperature to produce molten glass.” PC 4 at 1. The Agency incorporated this
recommendation in its first motion to amend its proposal. Mot. Amend 1 at 2.
Section 211.3100: Industrial Boiler
In its proposal, the Agency sought to add a definition of the term “industrial boiler,”
which is necessary for applicability under Subpart E. Statement at 15. In its entirety, the
proposed definition provided that
‘[i]ndustrial boiler’ means, for purposes of Part 217, an enclosed vessel in which
water is heated and circulated either as hot water or as steam for heating or for
power, or both. The term does not include boilers serving a generator that has a
nameplate capacity greater than 25 MWe and produces electricity for sale, and
cogeneration units, as that term is defined in Section 225.130 of Part 225, if such
boilers or cogeneration units are subject to the CAIR NO
x
Trading Programs
under Subpart D or E of Part 225. Prop. at 15 (proposed new Section 211.3100).
In a question filed for the first hearing on October 14, 2008, Midwest Generation
asked whether, in terms of definitions or use, the Agency intended in its proposed rule to
distinguish between industrial boilers, fossil fuel-fired boilers, and EGUs. MG Questions
at 1. In response, the Agency provided the following distinction: “EGU boilers are used
primarily to generate electricity to sell on the electricity grid. Industrial boilers are used

39
primarily to generate power (steam or electricity) for use at the source. Both types of
boilers may use fossil fuels, coal, oil, or gas.” MG Answers at 1.
In a question filed for the first hearing on October 14, 2008, IERG inquired
whether the Agency intended to include in the definition of “industrial boiler” either
“cogeneration units and/or heat recovery steam generators that capture waste heat from turbines
or engines.” IERG Questions at 4;
see
Prop. at 41-44 (proposed Subpart D). The Agency
responded simply “[y]es.” IERG Answers at 6. The Agency stated, however, that it had not
“performed any analysis to determine the technical feasibility and cost for cogeneration units
and/or heat recovery steam generators to comply with its proposed rule.”
Id.; see
Tr.1 at 66.
In another question filed for the first hearing on October 14, 2008, IERG inquired
whether the Agency intended to include in the definition of “industrial boiler” or “process
heater” those “gas-fired chillers that provide cooling for either processes or occupied spaces.”
IERG Questions at 4;
see
Prop. at 41-47. The Agency responded by stating that, “[i]f refrigerant
is heated [in]directly by gas heating, it is a process heater.” IERG Answers at 6;
see infra
at 27
(addressing proposed definition of “process heater”);
see also
Tr.1 at 68-69 (clarifying Agency
response). The Agency further stated that, although it had not “performed any analysis to
determine the technical feasibility and cost for such gas-fired chillers to comply with its
proposed rule,” it “believes that the technical feasibility and cost for gas-fired chillers should be
similar to process heaters and industrial boilers.” IERG Answers at 6-7,
see
Tr.1 at 67-68.
In a question filed for the first hearing on October 14, 2008, Midwest Generation first
stated that
[a]pplicability of Subpart M and the nonapplicability of Subpart D are premised
upon the applicability of the Part 225, Subparts C, D, and E (“the Illinois CAIR”)
to electric generating units (“EGUs”). However, the federal rule underlying the
Illinois CAIR has been overturned (assuming the D.C. Circuit Court issues the
mandate for its decision in appeal of the rule), thus invalidating the Illinois CAIR.
Therefore, it appears that EGUs, which the Agency apparently intended to cover
in Subpart M of this rulemaking, are covered by Subpart D. MG Questions at 2.
Midwest Generation then asked whether the Agency proposed to amend its language in Subpart
M. MG Answers at 2;
see
Prop. at 51-52 (proposed Subpart M). Although the Agency stated
that it disagreed “with the underlying premise of this question,” it indicated that it was
“amenable to amending” this definition of “industrial boiler” as described in response to a
subsequent question. MG Answers at 2;
see
Tr.1 at 190-92 (addressing status of federal rule).
In that subsequent question, Midwest Generation first stated that, “[b]ased upon the
proposed applicability language in Subpart M, Section 217.340, [and] assuming the D.C. Circuit
Court issues the mandate implementing its decision in the appeal of the CAIR, EGUs would be
subject to the provisions of Subpart D.” MG Questions at 3. Midwest Generation consequently
asked whether the Agency would consider amending its proposal to include the following
definition:

40
‘[i]ndustrial boiler’ means, for purposes of Part 217, an enclosed vessel in which
water is heated and circulated either as hot water or as steam for heating or for
power, or both. The term does not include boilers serving a generator that has a
nameplate capacity greater than 25 MWe and produces electricity for sale, and
cogeneration units, as that term is defined in Section 225.130 of Part 225, if such
boilers or cogeneration units are subject to the CAIR NO
x
Trading Programs
under Subpart D or E of Part 225.
Id
.
Responding to Midwest Generation, the Agency stated that it was “amenable” to amending its
proposed definition in the following fashion:
‘[i]ndustrial boiler’ means, for purposes of Part 217, an enclosed vessel in which
water is heated and circulated either as hot water or as steam for heating or for
power, or both. The term does not include boilers serving a generator that has a
nameplate capacity greater than 25 MWe and produces electricity for sale, and
cogeneration units, as that term is defined in Section 225.130 of Part 225, if such
boilers or cogeneration units are subject to meet the applicability criteria under
Subpart M of Part 217the CAIR NO
x
Trading Programs under Subpart D or E of
Part 225. MG Answers at 4-6.
During the first hearing on October 14, 2008, IERG posed the following question to the
Agency:
[i]f a heat recovery steam generator recovering heat from the exhaust of, A,
process, B, turbine, or C, engine, is considered a boiler for proposed – for this
proposed rule, then does the Agency intend to define the boiler’s rated heat input
capacity as a direct heat input to the heat recovery steam generator from
combustion of fuel in the heat recovery steam generator – for example, from a
duct burner – or does it intend to also include the heat input from the upstream
process in the rated capacity? Tr.1 at 65.
Responding in writing to this question, the Agency first stated that it had reviewed USEPA
regulations regarding turbines from which exhaust is captured in a heat recovery steam
generator. PC 1 at 1, citing 40 C.F.R. 60, Subparts GG, KKKK. The Agency stated that it had
decided “to treat a combustion turbine and heat recovery steam generator as a single unit.” PC 1
at 1. The Agency claims that this simplifies testing and monitoring NO
x
emissions.
Id
. The
Agency elaborated that
[t]he supplemental heat input of the duct burner/heat recovery steam generator
will be added to the heat input of the turbine. The combined heat input will be
subject to the applicable NO
x
emission limit for turbines under Subpart Q of Part
217. Therefore, the NO
x
emissions will be tested/monitored after the exhaust
from the heat recovery steam generator and shall comply with the NO
x
emission
limit for a turbine. However, the heat input of the duct burner/heat recovery
steam generator shall not be added to the heat input of the turbine to increase the
rated capacity of the turbine.
Id.
at 1-2.

41
The Agency accordingly proposed to amend the definition of “industrial boiler” by, among other
change, excluding “a heat recovery steam generator that captures waste heat from a combustion
turbine. . . . “
Id
. at 2.
In its first motion to amend its rulemaking proposal, the Agency recommended that the
Board “[a]mend Section 217.3100 by to reflect the provisions as previously agreed to between
the Illinois EPA and Midwest Generation as reflected in the Illinois EPA’s Answers to Midwest
Generation’s Questions for Agency Witnesses, filed September 30, 2008, and the October 14,
2008, hearing.” Mot. Amend 1 at 2;
see
MG Questions at 3, MG Answers at 4-6. In those
answers, the Agency had proposed to amend this definition to provide that
‘[i]ndustrial boiler’ means, for purposes of Part 217, an enclosed vessel in which
water is heated and circulated either as hot water or as steam for heating or for
power, or both. This term does not include boilers serving a generator that has a
nameplate capacity greater than 25MWe and produces electricity for sale, and
cogeneration units, as that term is defined in Section 225.120 of Part 225, if such
boilers or cogeneration units are subject to meet the applicability criteria under
Subpart M of Part 217 the CAIR NO
x
Trading Programs under Subpart D or E of
Part 225. MG Answers at 6;
but see
PC 1 at 2 (proposing to exclude from
definition heat recovery steam generators capturing waste heat from combustion
turbines).
In its post-hearing comments, Midwest Generation states that,
[w]ith the amendments proposed to the Board by the Agency in its Motion to
Amend Rulemaking Proposal ("Agency's Motion") filed January 30, 2009,
Midwest Generation generally supports the Agency's proposal as it applies to
electric generating units ("EGUs"). The proposed amendments incorporate by
reference provisions agreed to between the Agency and Midwest Generation as
part of the Agency's Answers to Midwest Generation's Questions for Agency
Witnesses ("Agency's Answers"), which were filed before this Board on
September 30, 2008. PC 9 at 1-2 (noting Agency’s amended proposed definition
of “industrial boiler”);
see
Mot. Amend 1 at 2;
see also
Tr.1 at 199-200.
In its second motion to amend its rulemaking proposal, the Agency recommended that the
Board accept the following amendment to this definition:
‘[i]ndustrial boiler’ means, for purposes of Part 217, an enclosed vessel in which
water is heated and circulated either as hot water or as steam for heating or for
power, or both. The term does not include a heat recovery steam generator that
captures waste heat from a combustion turbine and boilers serving a generator that
has a nameplate capacity greater than 25 MWe and produces electricity for sale, if
such boilers meet the applicability criteria under Subpart M of Part 217. Mot.
Amend 2 at 6.

42
The Agency states that this proposed amendment excludes from the definition “a heat recovery
steam generator that captures waste heat from a combustion turbine.” Mot. Amend 2 at 5. The
Agency further states that it proposed this amendment in post-hearing comments filed on
November 5, 2008, but inadvertently excluded it from the first motion to amend.
Id
. at 5, 6;
see
PC 1 at 1-2, citing Tr.1 at 65.
In its first notice comments, the Agency proposed to strike the reference to “cogeneration
units.” PC 17 at 1-2, citing In the Matter of: Nitrogen Oxides Emissions from Various Source
Categories: Amendments to 35 Ill. Adm. Code Parts 211 and 217, R08-19, slip op. at 26 (May 7,
2009). The Agency proposed the following language:
“industrial boiler” means, for purposes of Part 217, an enclosed vessel in which
water is heated and circulated either as hot water or as steam for heating or for
power, or both. This term does not include a heat recovery steam generator that
captures waste heat from a combustion turbine and boilers serving a generator that
has a nameplate capacity greater than 25 MWe and produces electricity for sale, if
such boilers meet the applicability criteria under Subpart M of Part 217. PC 17 at
1.
Section 211.3355: Lime Kiln
In its proposal, the Agency sought to add a definition of the term “lime kiln,” which is
necessitated by Subpart H. Statement at 15. In its entirety, the proposed definition states that
“‘[l]ime kiln’ means, for purposes of Part 217, an enclosed combustion device used to calcine
lime mud, which consists primarily of calcium carbonate, into calcium oxide.” Prop. at 15
(proposed new Section 211.3355).
Section 211.3475: Load Shaving Unit
In its proposal, the Agency sought to add a definition of the term “load shaving unit,”
which is included in the proposed definition of the term “auxiliary boiler.” Statement at 15. In
its entirety, the proposed definition states that “‘[l]oad shaving unit’ means, for purposes of Part
217, a device used to generate electricity for sale or use during high electric demand days,
including but not limited to stationary reciprocating internal combustion engines or turbines.”
Prop. at 15 (proposed new Section 211.3475).
In a question filed for the first hearing on October 14, 2008, Midwest Generation asked
the Agency whether the definition of “load shaving unit” includes a peaker power plant. MG
Questions at 2. The Agency responded simply “[y]es.” MG Answers at 2.
Section 211.4280: Other Glass
In its proposal, the Agency sought to add a definition of the term “other glass,” which is
necessitated by Subpart G. Statement at 15. In its entirety, the proposed definition states that
“‘[o]ther glass’ means, for purposes of Part 217, glass that is neither container glass, as that term

43
is defined in Section 211.1435, nor flat glass, as that term is defined in Section 211.2357.” Prop.
at 15 (proposed new Section 211.4280).
Section 211.5195: Process Heater
In its proposal, the Agency sought to add a definition of the term “process heater,” which
is necessitated by Subpart F. Statement at 15. In its entirety, the proposed definition states that
“‘[p]rocess heater’ means, for purposes of Part 217, an enclosed combustion device that burns
gaseous or liquid fuels only and that indirectly transfers heat to a process fluid or a heat transfer
medium other than water. This term does not include pipeline heaters and storage tank heaters
that are primarily meant to maintain fluids at a certain temperature or viscosity.” Prop. at 15-16
(proposed new Section 211.5195).
In a question filed for the first hearing on October 14, 2008, IERG inquired whether the
Agency intended to include in the definition of “industrial boiler” or “process heater” those “gas-
fired chillers that provide cooling for either processes or occupied spaces.” IERG Questions at 4;
see
Prop. at 41-47. The Agency responded by stating that, “[i]f refrigerant is heated [in]directly
by gas heating, it is a process heater.” IERG Answers at 6;
see
Tr.1 at 68-69 (clarifying Agency
response). The Agency further stated that, although it had not “performed any analysis to
determine the technical feasibility and cost for such gas-fired chillers to comply with its
proposed rule,” it “believes that the technical feasibility and cost for gas-fired chillers should be
similar to process heaters and industrial boilers.” IERG Answers at 6-7,
see
Tr.1 at 67-68.
Part 217: Nitrogen Oxides Emissions
Subpart A: General Provisions
Section 217.100: Scope and Organization.
Existing Section 217.100 sets forth the
scope and organization of Part 217. 35 Ill. Adm. Code 217.100. In its proposal, the Agency
sought only to “amend subsection (b) of this Section to state that permits for sources subject to
Part 217 may be required under Section 39.5 of the Act, in addition to 35 Ill. Adm. Code Part
201.” Statement at 15;
see
Prop. at 22;
see also
415 ILCS 5/39.5 (2008) (Clean Air Act Permit
Program).
Section 217.104: Incorporations by Reference.
Existing Section 217.104 incorporates
by reference various specified materials. 35 Ill. Adm. Code 217.104. In its proposal, the Agency
sought “to add test methods under 40 C.F.R. Part 60 and [USEPA] Alternative Control
Techniques Documents.” Statement at 16;
see
Prop. at 22-23.
In its first notice comments, the Agency sought to update one incorporation by reference
in proposed subsection (l) and to add two new incorporations by reference in proposed
subsections (q) and (r). PC 17 at 2.
Subpart B: New Fuel Combustion Emission Sources

44
Section 217.121: New Emission Sources.
Existing Section 217.121 addresses NO
x
emissions from new sources. 35 Ill. Adm. Code 217.121. In its proposal, the Agency sought “to
repeal this Section.” Statement at 16;
see
Prop. at 23-24;
see also
Tr.1 at 187.
Subpart C: Existing Fuel Combustion Emission Units
Section 217.141: Existing Emission Units in Major Metropolitan Areas.
Section
217.141 now regulates existing emission sources in major metropolitan areas. 35 Ill. Adm. Code
217.141. The Agency’s proposal first sought “to amend this Section by changing the term
‘source’ to ‘unit.’” Statement at 16;
see
Prop. at 25-26. The Agency also sought to add language
in a new subsection (d)(2) providing “that the Section does not apply to emission units that are
subject to the emissions limitations of Subpart D, E, F, G, H, M, or Q of Part 217.” Statement at
16;
see
Prop. at 26.
During the first hearing on October 14, 2008, counsel for Midwest Generation questioned
whether Section 217.141 would be necessary if the Board adopts this proposed rule. Tr.1 at 189.
The Agency responded that the Board originally promulgated this language in 1972 as Rule 207
and applied it to both new and existing sources. PC 1 at 4, citing In the Matter of: Emissions
Standards, R71-23. The Agency stated that
[t]he NO
x
limitations under Section 217.141 apply to any existing fuel
combustion emission source with an actual heat input equal to or greater than 73.2
MW (250 mmbtu/hr), located in the Chicago or St. Louis (Illinois) major
metropolitan areas. Currently, sources meeting the heat input criteria and located
in these areas are subject to these NO
x
limitations. Accordingly, these limitations
appear in sources’ permits. PC 1 at 4.
Subpart D: NO
x
General Requirements
In its first notice comments, the Agency proposed to “[a]mend the heading of Subpart D
of Part 217 by deleting the reference to ‘Industrial Boilers’ and adding “NO
x
General
Requirements.’” PC 17 at 2;
see
33 Ill. Reg. 6941 (May 22, 2009).
Section 217.150: Applicability.
In its original proposal, the Agency sought to add a
new Section 217.150 addressing the applicability of the proposed Subparts C, D, E, F, G, H, and
M of Part 217. Statement at 16;
see
Prop. at 26-27.
The proposed subsection (a)(1)(A) provides that Subparts E, F, G, H, I, and M apply to
all sources that are located in the two areas designated as nonattainment for the 8-hour ozone and
PM
2.5
standards and that emit or have the potential to emit NO
x
in an amount equal to or greater
than 100 tons per year. Statement at 10-11, 16;
see
Prop. at 26. The proposed subsection
(a)(1)(B) provides that Subparts E, F, G, H, I, and M also apply to “[a]ny industrial boiler,
process heater, glass melting furnace, cement kiln, lime kiln, iron and steel reheat, annealing, or
galvanizing furnace, aluminum reverberatory or crucible furnace, or fossil fuel-fired stationary
boiler at such sources [described in subsection (a)(1)(A)] that emits NO
x
in an amount equal to or

45
greater than 15 tons per year and equal to or greater than five tons per ozone season.” Statement
at 10-11, 16-17;
see
Prop. at 26, Gupta Pre-filed Test. at 2.
Noting that the proposed regulations would apply to both existing and new units, the
Agency stated that the existing units that would become subject to the regulations include the
following: “80 industrial boilers, 84 process heaters, four glass melting furnaces, two lime kilns,
six furnaces used in iron and steel making, and 20 fossil fuel-fired stationary boilers.” Statement
at 10;
see
TSD at 130-31 (describing affected sources). These 196 sources emitted 44,625 tons
of NO
x
in 2005, and the Agency projected that its proposal would reduce those emissions by
20,666 tons or 46.3%. TSD at 133 (Table 10-1), Gupta Pre-filed Test. at 3.
In a question filed for the first hearing on October 14, 2008, Midwest Generation noted
that the section employs the term “emits” in determining applicability. MG Questions at 1.
Midwest Generation asked how the Agency would determine “whether a unit emits, as opposed
to having the potential to emit, at the threshold levels.”
Id
. The Agency responded that, “[i]n
general, the Illinois EPA intends to rely on Annual Emission Reports submitted by
owners/operators of emission sources.” MG Answers at 2;
see
Tr.1 at 184-86.
In the second motion to amend its rulemaking proposal, the Agency sought to add a new
subsection providing in its entirety that “[f]or purposes of this Section, ‘potential to emit’ means
the quantity of NO
x
that potentially could be emitted by a stationary source before add-on
controls based on the design capacity or maximum production capacity of the source and 8,760
hours per year or the quantity of NO
x
that potentially could be emitted by a stationary source as
established in a federally enforceable permit.” Mot. Amend 2 at 6. The Agency stated that it
added this definition in response to comments by USEPA.
Id
. at 2.
In another question filed for the first hearing, Midwest Generation noted that Section
217.150(a) originally provided that “[t]he provisions of this Subpart and Subparts D, E, F, G, H,
and M apply to . . . [a]ll sources. . . .” MG Questions at 2;
see
Prop. at 26. Midwest Generation
asked whether the Agency intended “that all of these subparts actually apply to all sources in the
specified geographic areas.” MG Questions at 2-3. Specifically, Midwest Generation asked
whether the Agency instead intended “that only one subpart will apply to a unit or units at
threshold sources, as determined by the characteristics of the unit.”
Id
. at 3. The Agency
responded by stating its “intent that each respective Subpart apply to sources that meet the
applicability criteria and individual emission units at such sources that meet the applicability
criteria,
i.e.
, the provisions of a respective Subpart apply to the extent a source includes emission
units of the type covered under the Subpart.” MG Answers at 3.
In another question filed for the first hearing, Midwest Generation claimed that “[t]he ‘all
industrial boilers’ language in Section 217.160(a) and similar language in the other subparts
could be construed to expand the scope of [the original] Section 217.150(a)(2), which refers to
‘any industrial boiler [and other types of emission units] that emits NO
x
in an amount equal to or
greater than 15 tons per year and equal to or greater than five tons per ozone season.” MG
Questions at 2;
see
Prop. at 41-42 (proposed Section 217.160(a)). Midwest Generation
questioned whether the Agency intended “to expand the applicability of the rule in this way.”
MG Questions at 2. The Agency responded by expressing the intent “that each Subpart apply to

46
all of the affected emission units at an affected source,
e.g.
, ‘any’ emission unit that meets the
applicability criteria.” MG Answers at 3.
The Agency also proposed a new subsection (b) providing that, if a source ceases to
fulfill the emissions criteria of subsection (a) of this Section, the requirements of Subparts E, F,
G, H, I, or M of Part 217 continue to apply to any emission unit that was ever subject to the
provisions of any of those Subparts.
See
Statement at 17; Prop. at 26. The proposed subsection
(c) provides that “the provisions of this Subpart do not apply to afterburners, flares, and
incinerators.”
See
Statement at 17; Prop. at 27.
In addition, the Agency’s proposed subsection (d) provided that,
where a construction permit, for which the application was submitted to the
Agency prior to the adoption of Subpart C, is issued that relies on decreases in
emissions of NO
x
from existing emission units for purposes of netting or emission
offsets, such NO
x
decreases remain creditable notwithstanding any requirements
that may apply to the existing emission units pursuant to Subpart C and Subpart
D, E, F, G, H, or M of Part 217. Statement at 17;
see
Prop. at 27.
In the first motion to amend its rulemaking proposal, the Agency sought to add a
subsection (e) providing in its entirety that “[t]he owner or operator of an emission unit that is
subject to this Subpart and Subpart D, E, F, G, H, or M of this Part must operate such unit in a
manner consistent with good air pollution control practice to minimize NO
x
emissions.” Mot.
Amend 1 at 3. The Agency had originally included this language in the proposed subsection
217.152(b) regarding the compliance date. Prop. at 27;
see
Tr.1 at 196-98 (suggesting relocation
under applicability provisions).
Section 217.152: Compliance Date.
The Agency sought to add a new section regarding
the compliance date for its proposed rule. Statement at 17;
see
Prop. at 27. The proposed
subsection (a) originally provided “that compliance with the requirements of Subparts D, E, F, G,
H, and M by an owner or operator of an emission unit that is subject to any one of those subparts
is required beginning May 1, 2010.” Statement at 17;
see
Prop. at 27.
Proposed subsection (b) originally provided “that the first annual compliance period is
May 1, 2010, through April 30, 2011, and then on a calendar years basis thereafter.” Statement
at 17;
see
Prop. at 27. Subsection (b) also originally provided that “the owner or operator of an
emission unit that is subject to Subpart D, E, F, G, H, or M must operate such unit in a manner
consistent with good air pollution control practice to minimize NO
x
emissions.” Statement at 17;
see
Prop. at 27.
In a question filed for the first hearing on October 14, 2008, Midwest Generation asked
how the second sentence of subsection (b), regarding air pollution control practices, related to the
proposed compliance date. MG Questions at 3. Responding, the Agency simply stated that
“[t]here is no relation.” MG Answers at 3;
see
Tr.1 at 196-98 (suggesting relocation under
applicability provisions). In post-hearing comments, the Agency agreed “that it may be more
appropriate to place this sentence in another section. . . . PC 1 at 4.

47
In comments filed for the second hearing beginning December 9, 2008, Saint-Gobain
argued that “a narrow exception should be made to the May 1, 2010 compliance date for entities
that enter into an enforceable agreement with IEPA to install control technology that can achieve
NO
x
emission rates significantly below the 5.0 lbs/ton limit pursuant to an enforceable schedule
extending beyond 2010.” PC 4 at 1. Saint-Gobain states that it “is currently in the process of
negotiating such an agreement with IEPA.”
Id
. Saint-Gobain specifically proposed that Section
217.152 include a new subsection providing in its entirety that,
[n]otwithstanding subsections (a), (b), and (c) of this Section, compliance with the
requirements of Subpart F of this Part by an owner or operator of an emission unit
subject to Subpart F of this Part shall be extended until December 31, 2014, if
such units are required to meet emissions limitations for NO
x
, as measured using a
continuous emissions monitoring system, and included within a legally
enforceable order on or before December 31, 2009, whereby such emissions
limitations are less than 30 percent of the emissions limitations set forth under
Section 217.204 of Subpart F of this Part.
Id
. at 2.
Saint-Gobain supported its proposed language by stating that it
cannot afford to install the technology required to meet an interim limit of 5.0
lbs/ton for the period between the compliance date under Section 217.204 and the
anticipated schedule for installation of the alternative technology at the end of
2014, and thus the opportunity for substantially greater long-term emission
reductions may be lost if a limited exemption from the May 1, 2010 compliance
date is not adopted.
Id
. at 1.
Saint-Gobain also argued that early installation of CEMS would require significantly greater
expense than later installation with the alternative technology and “would serve no compliance
purpose.”
Id
. at 2.
Participants doubted that sources could achieve compliance by the Agency’s proposed
compliance deadline and proposed alternative compliance schedules.
E.g.
, Exh. 5 at 15-16
(IERG). Exh. 6 at 12-15 (IERG), Exh. 9 at 3-6 (ConocoPhillips), Exh. 10 at 7-8 (U.S. Steel). In
the first motion to amend its rulemaking proposal, the Agency proposed to amend subsection (a)
to provide in its entirety that “[c]ompliance with the requirements of Subparts D, E, F, G, H, and
M by an owner or operator of an emission unit that is subject to Subpart D, E, F, G, H, or M is
required beginning January 1, 2012.” Mot. Amend 1 at 2, 3.
The first motion to amend also sought to amend subsection (b) to provide in its entirety
that
[n]otwithstanding subsection (a) of this Section, compliance with the
requirements of Subpart F of this Part by an owner or operator of an emission unit
subject to Subpart F of this Part shall be extended until December 31, 2014, if
such units are required to meet emissions limitations for NO
x
, as measured using a

48
continuous emissions monitoring system, and included within a legally
enforceable order on or before December 31, 2009, whereby such emissions
limitations are less than 30 percent of the emissions limitations set forth under
Section 217.204 of Subpart F of this Part. Mot. Amend 2 at 2, 3.
In the second motion to amend its proposal, the Agency sought to add a subsection (c)
providing in its entirety that,
[n]otwithstanding subsection (a) of this Section, the owner or operator of emission
units subject to Subpart D or E of this Part and located at a petroleum refinery
must comply with the requirements of this Subpart and Subpart D or E of this
Part, as applicable, for those emission units beginning January 1, 2012, except
that the owner or operator of emission units listed in Appendix H must comply
with the requirements of this Subpart, including the option of demonstrating
compliance with the applicable Subpart through an emissions averaging plan
under Section 217.158 of this Subpart, and Subpart D or E of this Part, as
applicable, for the listed emission units beginning on the dates set forth in
Appendix H. With Agency approval, the owner or operator of emission units
listed in Appendix H may elect to comply with the requirements of this Subpart
and Subpart D or E of this Part, as applicable, by reducing the emissions of
emission units other than those listed in Appendix H, provided that the emissions
limitations of such other emission units are equal to or more stringent than the
applicable emissions limitations set forth in Subpart D or E of this Part, as
applicable, by the dates set forth in Appendix H. Mot. Amend 2 at 2, 6-7;
see
Mot. Amend 2 at 13-14 (proposed Appendix H).
Section 217.154: Performance Testing.
The Agency sought to add a new section
regarding performance testing requirements for units subject to Subparts D, E, F, G, or H.
Statement at 18-19;
see
Prop. at 27-28. Proposed subsection (a) originally provided “that such
testing for emission units constructed on or before December 1, 2009, and subject to one of those
subparts must be conducted in accordance with Section 217.157.” Statement at 18;
see
Prop. at
27. Subsection (a) also provided an exception from this requirement for owners and operators
demonstrating compliance through CEMS. Statement at 18;
see
Prop. at 27.
Proposed subsection (b) provided that “performance testing of NO
x
emissions for
emission units constructed or modified after December 1, 2009, and subject to one of those
subparts must be conducted within 60 days of achieving maximum operating rate but no later
than 180 days after initial startup of the new or modified emission units, in accordance with
Section 217.157.” Statement at 18;
see
Prop. at 27. Subsection (b) also provided an exception
for owners and operators demonstrating compliance through CEMS. Statement at 18;
see
Prop.
at 28.
In a question filed for the first hearing on October 14, 2008, IERG noted that subsection
(a) and (b) “refer to the date of emission unit construction or modification” and asked the
Agency to clarify the meaning of the terms “constructed on or before” and “construction or
modification occurs after.” IERG Questions at 16-17. Specifically, IERG asked whether the

49
Agency refers to “the beginning of construction, the completion of construction, [or] the date of
issuance of a construction permit?”
Id
.
In its response, the Agency first noted that definitions in Parts 201 and 211 apply to Part
217. IERG Answers at 9;
see
35 Ill. Adm. Code 201, 211, 217.103. The Agency further noted
that Section 201.102 defines “construction” as “commencement of on-site fabrication, erection
or installation of an emission source or of air pollution control equipment.” IERG Answers at 9,
citing 35 Ill. Adm. Code 201.102. The Agency also notes that it defines “modification” as
any physical change in, or change in the method of operations, of an emission
source or of air pollution control equipment which increases the amount of any
specified air contaminant emitted by such source or equipment or which results in
the emission of any specified air contaminant not previously emitted. It shall be
presumed that an increase in the use of raw materials, the time of operation or the
rate of production will change the amount of any specified air contaminant
emitted. Notwithstanding any other provisions of this definition, for purposes of
permits issued pursuant to Subpart D, the Illinois Environmental Agency
(Agency) may specify conditions under which an emission source or air pollution
control equipment may be operated without causing a modification as herein
defined, and normal cyclical variations, before the date operating permits are
required, shall not be considered modifications. IERG Answers at 9, citing 35 Ill.
Adm. Code 201.102.
The Agency suggests that these definitions determine what constitutes the beginning or the
completion of construction. IERG Answers at 9.
In its first motion to amend its proposal, the Agency sought to replace subsection (a) with
the following language:
[p]erformance testing of NO
x
emissions for emission units constructed on or
before July 1, 2011, and subject to Subpart D, E, F, G, or H of this Part must be
conducted in accordance with Section 217.157 of this Subpart. This subsection
does not apply to owners and operators of emission units demonstrating
compliance through a continuous emissions monitoring system. Mot. Amend 1 at
3.
In its first notice comment, the Agency proposed to clarify subsection (a) by adding
“references to ‘emission limitations under’ an applicable Subpart and to add the exclusion for a
‘predictive emission monitoring system, or combustions tuning.’” PC 17 at 2. Specifically, the
Agency proposed the following language:
[p]erformance testing of NO
x
emissions for emission units constructed on or
before July 1, 2011, and subject to emissions limitations under Subpart E, F, G, H,
or I of this Part must be conducted in accordance with Section 217.157 of this
Subpart. Except as provided for under Section 217.157(a)(4) and (e)(1), this
subsection does not apply to owners and operators of emission units

50
demonstrating compliance through a continuous emission monitoring system,
predictive emission monitoring system, or combustion tuning. PC 17 at 2-3.
Also in the first motion to amend, the Agency sought to replace subsection (b)
with the following language:
[p]erformance testing of NO
x
emissions for emission units for which construction
or modification occurs after July1, 2011, and that are subject to Subpart D, E, F,
G, or H of this Part must be conducted within 60 days of achieving maximum
operating rate but no later than 180 days after initial startup of the new or
modified emission unit, in accordance with Section 217.157 of this Subpart. This
subsection does not apply to owners and operators of emission units
demonstrating compliance through a continuous emissions monitoring system.
Mot. Amend 1 at 3.
In its first notice comment, the Agency proposed to clarify subsection (b) by adding
“references to ‘emission limitations under’ an applicable Subpart and to add the exclusion for a
‘predictive emission monitoring system, or combustions tuning.’” PC 17 at 2. Specifically, the
Agency proposed the following language:
[p]erformance testing of NO
x
emissions for emission units for which construction
or modification occurs after July 1, 2011, and subject to emissions limitations
under Subpart E, F, G, H, or I of this Part must be conducted within 0 days of
achieving maximum operating rate but no later than 180 days after initial startup
of the new or modified emission unit, in accordance with Section 217.157 of this
Subpart. Except as provided for under Section 217.157(a)(4) and (e)(1), this
subsection does not apply to owners and operators of emission units
demonstrating compliance through a continuous emission monitoring system,
predictive emission monitoring system, or combustion tuning. PC 17 at 2-3.
Proposed subsection (c) provides that notification of initial startup of a unit subject to
subsection (b) “must be provided to the Agency no later than 30 days after initial startup.”
Statement at 18;
see
Prop. at 28. Proposed subsection (d) provides that the owner or operator of
a unit subject to subsection (a) or (b) “must notify the Agency of the scheduled date for the
performance testing at least 30 days in writing before such date and five days before such date.”
Statement at 18;
see
Prop. at 28.
Proposed subsection (e) provides that, “if demonstrating compliance through a emissions
averaging plan, at least 30 days before changing the method of compliance, the owner or
operator of an emission unit must submit a written notification to the Agency describing the new
method of compliance, the reason for the change in the method of compliance, and the scheduled
date for the compliance demonstration testing, if required.” Statement at 18-19;
see
Prop. at 28.
Subsection (e) also provides that an owner or operator changing the method of compliance “must
submit to the Agency a revised compliance certification that meets the requirements of Section
217.155.” Statement at 19;
see
Prop. at 28.

51
Section 217.155: Initial Compliance Certification.
The Agency sought to add a new
section regarding initial compliance certification for units subject to Subpart D, E, F, G, H, or M.
Statement at 19-20:
see
Prop. at 28-29. As originally proposed, subsection (a) provided that, by
May 1, 2010, the owner or operator of a unit subject to Subpart D, E, F, G, H, or M who does not
demonstrate compliance with CEMS “must certify to the Agency that the emission unit will be in
compliance with the applicable emissions limitation of Subpart D, E, F, G, or H of Part 217
beginning May 1, 2010.” Statement at 19;
see
Prop. at 28. The subsection also provided that
“certification must include the results of the performance testing performed in accordance with
Sections 217.154(a) and (b) of Subpart C and the calculations necessary to demonstrate that the
subject emission unit will be in initial compliance.” Statement at 19;
see
Prop. at 28.
In the first motion to amend its rulemaking proposal, the Agency sought to replace
subsection (a) with the following language:
[b]y the applicable compliance date set forth under Section 217.152 of this
Subpart, an owner or operator of an emission unit subject to Subpart D, E, F, G,
or H of this Part who is not demonstrating compliance through the use of a
continuous emissions monitoring system must certify to the Agency that the
emission unit will be in compliance with the applicable emissions limitation of
Subpart D, E, F, G, or H of this Part beginning on such applicable compliance
date. The performance testing certification must include the results of the
performance testing performed in accordance with Sections 217.154(a) and (b) of
this Subpart and the calculations necessary to demonstrate that the subject
emission unit will be in initial compliance. Mot. Amend 1 at 4.
As originally proposed, subsection (b) provided that, by May 1, 2010, the owner or
operator of a unit subject to Subpart D, E, F, G, H, or M who is demonstrating compliance with
CEMS “must certify to the Agency that the affected emission units will be in compliance with
the applicable emissions limitation of Subpart D, E, F, G, or H of Part 217 beginning May 1,
2010.” Statement at 19;
see
Prop. at 28. The subsection also provided that “[s]uch compliance
certification must include a certification of the installation and operation of a continuous
emissions monitoring system required under Sections 217.157 of Subpart C and the monitoring
data necessary to demonstrate that the subject emission unit will be in initial compliance.”
Statement at 19-20;
see
Prop. at 28-29.
In the first motion to amend its rulemaking proposal, the Agency sought to replace
subsection (b) with the following language:
[b]y the applicable compliance date set forth under Section 217.152 of this
Subpart, an owner or operator of an emission unit subject to Subpart D, E, F, G,
H, or M of this Part who is demonstrating compliance through the use of a
continuous emissions monitoring system must certify to the Agency that the
affected emission units will be in compliance with the applicable emissions
limitation of Subpart D, E, F, G, H, or M of this Part beginning on such applicable
compliance date. The compliance certification must include a certification of the
installation and operation of a continuous emissions monitoring system required

52
under Section 217.157 of this Subpart and the monitoring data necessary to
demonstrate that the subject emission unit will be in initial compliance. Mot.
Amend 1 at 4;
see also
PC 2 at 1 (proposing extension of compliance deadline for
CEMS).
Section 217.156: Recordkeeping and Reporting.
The Agency sought to add a new
section regarding recordkeeping and reporting by owners or operators of sources subject to
Subpart D, E, F, G, H, or M. Statement at 20-23:
see
Prop. at 29-32. The proposed subsection
(a) provided that such owners or operators “must keep and maintain all records used to
demonstrate initial compliance and ongoing compliance with the requirements of these
Subparts.” Statement at 20;
see
Prop. at 29. The subsection also provided that, “except as
otherwise provided under those Subparts, copies of such records must be submitted by the owner
or operator of the source to the Agency within 30 days after receipt of a written request by the
Agency, and such records must be kept at the source and maintained for at least five years and
must be available for inspection and copying by the Agency.” Statement at 20;
see
Prop. at 29
(proposed subsections (a)(1) and (a)(2)).
Proposed subsection (b) provided that the owner or operator of a unit subject to Subpart
D, E, F, G, H, or M must maintain records, including eleven specific items, demonstrating
compliance with the applicable subpart. Statement at 20-21;
see
Prop. at 29-30. Specifically,
subsection (b)(8) requires that records include “[a] log of all maintenance and inspections related
to the unit’s air pollution control equipment for NO
x
that it performed on the unit.” Prop. at 30;
see
Statement at 20-21. Also, subsection (b)(9) requires that records include “[a] log for the NO
x
monitoring device, if present, including periods when not in service and maintenance and
inspection activities that are performed on the device.” Prop. at 30;
see
Statement at 21.
In a question filed for the first hearing on October 14, 2008, Midwest Generation asked
whether “the recordkeeping systems that sources already have in place comprise the ‘logs’
required at Sections 217.156(b)(8) and (9), assuming all of the information required by the rule is
included?” MG Questions at 2. The Agency responded that they do comprise the required logs,
“as long as all of the required information under the rule is included.” MG Answers at 3.
Proposed subsection (c) provided in its entirety that “[t]he owner or operator of an
industrial boiler subject to Subpart D of this Part must maintain records in order to demonstrate
compliance with the combustion tuning requirements under Section 217.166 of this Part.” Prop.
at 30;
see
Statement at 21. Proposed subsection (d) provided in its entirety that “[t]he owner or
operator of a process heater subject to Subpart E of this Part must maintain records in order to
demonstrate compliance with the combustion tuning requirements under Section 217.186 of this
Part.” Prop. at 30;
see
Statement at 21. Proposed subsection (e) provided in its entirety that
“[t]he owner or operator of an emission unit subject to Subpart D, E, F, G, H, or M of this Part
must maintain records in order to demonstrate compliance with the testing and monitoring
requirements under Section 217.157 of this Subpart.” Prop. at 30;
see
Statement at 21.
Proposed subsection (f) provided that an owner or operator of a unit subject to Subparts
D, E, F, G, or H must provide four specific submissions with respect to performance testing
under Section 217.157(a)(4) and (b)(2). Prop. at 30-31;
see
Statement at 21-22. In the second

53
motion to amend its rulemaking proposal, the Agency sought to amend subsection (f) to provide
that recordkeeping and reporting, as they pertain to performance testing, applies “to all
performance testing conducted under Section 217.157 and not just certain testing as under the
original proposal.” Mot. Amend 2 at 2;
see
Prop. at 30-31.
Proposed subsection (g) provided that “the owner or operator of an emission unit subject
to Subpart D, E, F, G, H, or M must notify the Agency of any exceedances of an applicable
emissions limitation of Subpart D, E, F, G, H, or M by sending the applicable report with an
explanation of the causes of such exceedances to the Agency within 30 days following the end of
the applicable compliance period in which the emissions limitation was not met.” Statement at
22;
see
Prop. at 31. In a question filed for the first hearing on October 14, 2008, Midwest
Generation asked what constitutes the “applicable compliance period.” MG Questions at 2. The
Agency responded that that period is “[t]he annual or ozone season compliance period.” MG
Answers at 3.
Proposed subsection (h) provided that, “within 30 days of a written request by the
Agency, the owner or operator of an emission unit that is exempt from the requirements of
Subpart D, E, F, G, H, or M must submit records that document that the emission unit is exempt
from those requirements to the Agency.” Statement at 22;
see
Prop. at 31. Proposed subsection
(i) provided that an owner or operator complying through an emissions averaging plan must
submit by March 1 following the applicable calendar year a report demonstrating four specific
items. Prop. at 31;
see
Statement at 22. Proposed subsection (j) provided that an owner or
operator complying through the use of CEMS must submit to the Agency within 30 days after
the end of each calendar quarter a report including two specified items of information. Prop. at
32;
see
Statement at 23.
Proposed subsection (k) provided that “the owner or operator of an emission unit subject
to Subpart M must comply with the compliance certification and recordkeeping and reporting
requirements in accordance with 40 C.F.R. 96, or an alternate procedure approved by the Agency
and USEPA.” Statement at 23;
see
Prop. at 32. In a question filed for the first hearing on
October 14, 2008, Midwest Generation asked whether subsection (k) “supersede[s] the other
recordkeeping and reporting requirements of Section 217.156?” MG Questions at 2.
Responding, the Agency stated that its “intent is that electric generating units subject to Subpart
M comply with the compliance certifications, recordkeeping, and reporting requirements
pursuant to 40 C.F.R. 96, in conjunction with the other recordkeeping and reporting requirements
under Section 217.156, to the extent the requirements are not duplicative.” MG Answers at 4.
Section 217.157: Testing and Monitoring.
The Agency sought to add a new section
regarding testing and monitoring by owners or operators of sources subject to Subpart D, E, F, G,
H, or M. Statement at 20-27:
see
Prop. at 32-37. The proposed subsection (a) “includes the
provisions applicable to owners and operators of industrial boilers subject to Subpart D and
process heaters subject to Subpart E.” Statement at 23;
see
Prop. at 32-34.
Proposed subsection (a)(1) provided that “the owner or operator of an industrial boiler
subject to Subpart D with a rated heat input capacity greater than 250 mmBtu/hr must install,
calibrate, maintain, and operate a continuous emissions monitoring system on the emission unit

54
for the measurement of NO
x
emissions discharged into the atmosphere in accordance with 40
C.F.R. Part 75.” Statement at 23;
see
Prop. at 32.
Proposed subsection (a)(2) provided that
the owner or operator of an industrial boiler subject to Subpart D with a rated heat
input capacity greater than 100 mmBtu/hr but less than or equal to 250 mmBtu/hr
must install, calibrate, maintain, and operate a continuous emissions monitoring
system on the emission unit for the measurement of NO
x
emissions discharged
into the atmosphere in accordance with 40 C.F.R. Part 60, Subpart A, and
Appendix B, Performance Specifications 2 and 3, and Appendix F, Quality
Assurance Procedures. Statement at 24;
see
Prop. at 32-33.
Proposed subsection (a)(3) provided that
the owner or operator of a process heater subject to Subpart E with a rated heat
input capacity greater than 100 mmBtu/hr must install, calibrate, maintain, and
operate a continuous emissions monitoring system on the emission unit for the
measurement of NO
x
emissions discharged into the atmosphere in accordance
with 40 C.F.R. Part 60, Subpart A, and Appendix B, Performance Specifications 2
and 3, and Appendix F, Quality Assurance Procedures. Statement at 24;
see
Prop.
at 33.
In testimony filed on behalf of ConocoPhillips for the second hearing on December 9,
2008, Mr. Dunn noted that the Agency’s proposal requiring installation of CEMS on any
industrial boiler or process heater over 100 mmBtu/hr would result in total estimated costs of
$12 million. Exh. 9 at 14-15. Mr. Dunn recommended that the Agency limit CEMS
requirements to units greater than 250 mmBtu/hr.
Id
. at 15. He also expressed the view that
“annual performance testing is sufficient for process heaters that are included in an averaging
plan.”
Id
. In post-hearing comments filed on March 23, 2009, ConocoPhillips noted that these
issues remained outstanding concerns with the Agency. PC 14 at 2-3.
Proposed subsection (a)(4) provided that, “if demonstrating compliance through an
emissions averaging plan, the owner or operator of an industrial boiler subject to Subpart D, or a
process heater subject to Subpart E, with a rated heat input capacity less than or equal to 100
mmBtu/hr and not demonstrating compliance through a continuous emission monitoring system
must have an initial performance test.” Statement at 24;
see
Prop. at 33. Proposed subsection
(a)(4)(A) establisheed the timing for the required subsequent performance tests. Statement at 24;
see
Prop. at 33. Proposed subsection (a)(4)(B) originally established other requirements for
these tests. Statement at 24;
see
Prop. at 33-34. In the first motion to amend its rulemaking
proposal, the Agency proposed to replace that language with the following:
[t]he owner or operator of an industrial boiler or process heater must have a
performance test conducted using 40 CFR Part 60, Subpart A, and Appendix A,
Method 1, 2, 3, 4, 7E, or 19, as incorporated by reference in Section 217.104 of
this Part, or other alternative USEPA methods approved by the Agency. Each

55
performance test must consist of three separate runs, each lasting a minimum of
60 minutes. NO
x
emissions must be measured while the industrial boiler is
operating at maximum operating capacity or while the process heater is operating
at normal maximum load. If the industrial boiler or process heater has combusted
more than one type of fuel in the prior year, a separate performance test is
required for each fuel. If a combination of fuels is typically used, a performance
test may be conducted with Agency approval on such combination of fuels
typically used. Except as provided under subsection (e) of this Section, this
subsection (a)(4)(B) of this Section does not apply if such owner or operator is
demonstrating compliance with an emissions limitation through a continuous
emissions monitoring system under subsection (a)(1), (a)(2), (a)(3), or (a)(5)) of
this Section. Mot. Amend 1 at 4-5.
Proposed subsection (a)(5) provided that, instead of complying with subsection (a)(4),
(a)(4)(A), and (a)(4)(B), “an owner or operator of an industrial boiler subject to Subpart D of this
Part, or a process heater subject to Subpart E of this Part, with a rated heat input capacity less
than or equal to 100 mmBtu/hr may install and operate a continuous emissions monitoring
system that meets the applicable requirements of 40 C.F.R. Part 60, Subpart A, and Appendix B,
Performance Specifications 2 and 3, and Appendix F, Quality Assurance Procedures.” Statement
at 25;
see
Prop. at 34. The proposed subsection further provided that the CEMS “must be used to
demonstrate compliance with the applicable emissions limitation or emissions averaging plan on
an ozone season and annual basis.” Statement at 25;
see
Prop. at 34.
Proposed subsection (a)(6) provided that, notwithstanding subsection (a)(2), the owner or
operator of an auxiliary boiler subject to Subpart D “with a rated heat input capacity less than or
equal to 250 mmBtu/hr and a capacity factor of less than or equal to 20% is not required to
install, calibrate, maintain, and operate a continuous emissions monitoring system on such boiler
for the measurement of NO
x
emissions discharged into the atmosphere, but must comply with the
performance test requirements under subsections (a)(4), (a)(4)(A), and (a)(4)(B) of this Section.”
Statement at 25;
see
Prop. at 34.
The proposed subsection (b) included provisions applicable to owners and operators of
glass melting furnaces subject to Subpart F, cement and lime kilns subject to Subpart G, iron and
steel reheat, annealing, or galvanizing furnaces subject to Subpart H, and aluminum
reverberatory and crucible furnaces subject to Subpart H. Statement at 25;
see
Prop. at 34.
Proposed subsection (b)(1) provided that
an owner or operator of such an emission unit that has the potential to emit NO
x
in
an amount equal to or greater than one ton per day must install, calibrate,
maintain, and operate a continuous emissions monitoring system on each such
emission unit for the measurement of NO
x
emissions discharged into the
atmosphere in accordance with 40 C.F.R. Part 60, Subpart A, and Appendix B,
Performance Specifications 2 and 3, and Appendix F, Quality Assurance
Procedures. Statement at 25-26;
see
Prop. at 34-35.

56
Proposed subsection (b)(2) provided that “an owner or operator of a glass melting
furnace, cement kiln or lime kiln, iron and steel reheat, annealing, or galvanizing furnace, or
aluminum reverberatory and crucible furnace that has the potential to emit NO
x
in an amount less
than one ton per day must have an initial performance test conducted” pursuant to subsection
(b)(4) and Section 217.154. Statement at 26;
see
Prop. at 35. Proposed subsection (b)(3)
establisheed the timing for the required subsequent performance tests. Statement at 26;
see
Prop.
at 35.
Proposed subsection (b)(4) originally established methods and requirements for those
performance tests. Statement at 26;
see
Prop. at 36. In comments filed on January 20, 2009,
Saint-Gobain proposed to amend that language by adding a sentence providing that, if a unit
demonstrates compliance with NO
x
limitations by CEMS under subsection (b)(1), then this
subsection (b)(4) does not apply. PC 4 at 1. In the first motion to amend its rulemaking
proposal, the Agency proposed to replace that language with the following:
The owner or operator of a glass melting furnace, cement kiln, or lime kiln must
have a performance test conducted using 40 CFR Part 60, Subpart A, and
Appendix A, Methods 1. 2, 3, 4, and 7E, as incorporated by reference in Section
217.104 of this Part, or other alternative USEPA methods approved by the
Agency. The owner or operator of an iron and steel reheat, annealing, or
galvanizing furnace, or aluminum reverberatory or crucible furnace must have a
performance test conducted using 40 CFR Part 60, Subpart A, and Appendix A,
Method 1, 2, 3, 4, 7E, or 19, as incorporated by reference in Section 217.104 of
this Part, or other alternative USEPA methods approved by the Agency. Each
performance test must consist of three separate runs, each lasting a minimum of
60 minutes. NO
x
emissions must be measured while the glass melting furnace,
cement kiln, lime kiln, iron and steel reheat, annealing, or galvanizing furnace, or
aluminum reverberatory or crucible furnace is operating at maximum operating
capacity. If the glass melting furnace, cement kiln, lime kiln, iron and steel
reheat, annealing, or galvanizing furnace, or aluminum reverberatory or crucible
furnace has combusted more than one type of fuel in the prior year, a separate
performance test is required for each fuel. Except as provided under subsection
(e) of this Section, this subsection (b)(4) of this Section does not apply if such
owner or operator is demonstrating compliance with an emissions limitation
through a continuous emissions monitoring system under subsection (b)(1) or
(b)(5) of this Section. Mot. Amend 1 at 5;
see infra
at 57 (noting proposed
addition of subsection (e));
see also
PC 4 at 1 (Saint-Gobain pre-hearing
proposal).
Proposed subsection (b)(5) provided that, instead of complying with subsections (b)(2),
(b)(3), and (b)(4),
an owner or operator of a glass melting furnace, cement kiln or lime kiln, iron and
steel reheat, annealing, or galvanizing furnace, or aluminum reverberatory and
crucible furnace that has the potential to emit NO
x
in an amount less than one ton
per day may install and operate a continuous emissions operating system on such

57
emission unit that meets the applicable requirements of 40 C.F.R. Part 60, Subpart
A, and Appendix B, Performance Specifications 2 and 3, and Appendix F, Quality
Assurance Procedures. Statement at 26;
see
Prop. at 36.
The proposed subsection also provides that the CEMS “must be used to demonstrate compliance
with the applicable emissions limitation or emissions averaging plan on an ozone season and
annual basis.” Statement at 26;
see
Prop. at 36.
Proposed subsection (c) provided in its entirety that “[t]he owner or operator of a fossil
fuel-fired stationary boiler subject to Subpart M of this Part must install, calibrate, maintain, and
operate a continuous emissions monitoring system on such emission unit for the measurement of
NO
x
emissions discharged into the atmosphere in accordance with 40 C.F.R. Part 96, Subpart
H.” Prop. at 36;
see
Statement at 27.
Proposed subsection (d) provided in its entirety that,
[i]f two or more emission units subject to Subpart D, E, F, G, H, M, or Q of this
Part are served by a common stack and the owner or operator of such emission
units is operating a continuous emissions monitoring system, the owner or
operator may, with written approval from the Agency, utilize a single continuous
emissions monitoring system for the combination of emission units subject to
Subpart D, E, F, G, H, M, or Q of this Part that share the common stack, provided
such emission units are subject to an emissions averaging plan under this Part.
Prop. at 37;
see
Statement at 27.
In its first motion to amend its rulemaking proposal, the Agency proposed to add a
subsection (e) to extend the deadline for the installation of CEMS. Mot. Amend 1 at 5;
see
Exh.
6 at 21 (urging additional time for installation), Exh. 9 (supporting three-year extension for
installation). In its second motion to amend, the Agency proposed to amend subsection (e) to
allow additional time for installation of CEMS. Mot. Amend 2 at 2, 7-8. The Agency also
proposed to add a subsection (f) allowing “for a predictive emission monitoring system, in
accordance with 40 C.F.R. Part 60, Subpart A, and Appendix B, Performance Specification 16,
as an alternative to the CEMS requirements for the owners or operators of certain emission units
who are not otherwise required by any other statute, regulation, or enforceable order to install a
CEMS on an emission unit.” Mot. Amend 2 at 2-3, 7-8.
Section 217.158: Emissions Averaging Plans.
The Agency sought to add a new section
regarding emissions averaging plans. Statement at 27-29:
see
Prop. at 37-41. Generally,
“[s]ources may aggregate and then average the NO
x
emissions from units at the same location in
Illinois to comply with the emissions limitations. . . .” Kaleel Pre-filed Test. at 3. Specifically,
proposed subsection (a) provided that, “[n]otwithstanding any other emissions averaging plan
provisions under this Part, an owner or operator of a source with certain emission units subject to
Subpart D, E, F, G, H, or M of this Part, or subject to Subpart Q of this Part that are located in
either one of the areas set forth under Section 217.150(a)(1)(A) or (B) of this Subpart, may
demonstrate compliance with the applicable Subpart through an emissions averaging plan.”
Prop. at 37;
see
Statement at 27.

58
In its first notice comments, the Agency proposed to correct the reference to “Section
217.150(a)(1)(A) or (B)” to read as “Section 217.150(a)(1)(A)(i) or (ii).” PC 17 at 3;
see
33 Ill.
Reg. 6941 (May 22, 2009) (reorganizing proposed Section 217.150).
The proposed subsection also provided that “[a]n emissions averaging plan can only
address emission units that are located at one source and each unit may only be covered by one
emissions averaging plan.” Prop. at 37;
see
Statement at 27, Tr.1 at 180. In a question filed for
the first hearing on October 14, 2008, Midwest Generation asked whether the Agency intended
to preclude “a unit that is in an averaging plan under this rule from participating in averaging
plans under other rules and
vice versa.
” MG Questions at 1. The Agency responded that it
intends “that an emission unit be included in only one seasonal and one annual averaging plan.
Units affected by Subpart Q (Engine Rule) can be included in an averaging plan with units
affected by this proposal.” MG Answers at 2;
see
Tr.1 at 181. Finally, the proposed subsection
also provides that “[s]uch emission units at the source are affected units and are subject to the
requirements of this Section.” Prop. at 37;
see
Statement at 27.
Proposed subsection (a)(1) described units that may be included in an emissions
averaging plan. Statement at 27;
see
Prop. at 37. First, under subsection (a)(1)(A), a plan may
include “[u]nits that commenced operation on or before January 1, 2002.” Prop. at 37;
see
Statement at 27. In a question filed for the first hearing on October 14, 2008, ExxonMobil asked
how the Agency set that date as a cutoff. ExxonMobil Questions at 4-5;
see
IERG Questions at
4. The Agency responded that “USEPA has established 2002 as the base year for planning
purposes for implementation of the ozone and PM
2.5
NAAQS established in 1997. States are
required to demonstrate continued progress towards attainment beginning in that year. The
Illinois EPA is seeking emission reductions from emission units that were in existence in 2002.”
ExxonMobil Answers at 5. The Agency acknowledged that new units may, under various
requirements, “have installed NO
x
control measures that are equal to or more stringent than the
proposed emission limitations here.”
Id
. at 6. The Agency stated, however, that “[i]f such units
were included in an averaging plan with units that existed in 2002, then the existing units may
not need to reduce emissions. This is counter to the objective of achieving Reasonable Further
Progress between 2002 and the attainment year, 2010.
Id
.;
see
IERG Answers at 8.
Under proposed subsection (a)(1)(B), a plan may include “[u]nits that the owner or
operator may claim as exempt under Subpart D, E, F, G, H, or M, as applicable, but does not
claim as exempt.” Statement at 27-28;
see
Prop. at 37. The proposed subsection also provided
that, “[f]or as long as such a unit is included in an emissions averaging plan, it will be treated as
an affected unit and subject to the applicable emissions limitations, and testing, monitoring,
recordkeeping, and reporting requirements.” Prop. at 37.
Under proposed subsection (a)(1)(C), a plan may include “[u]nits that commence
operation after January 1, 2002, if the unit replaces a unit that commenced operation on or before
January 1, 2002, or it replaces a unit that replaced a unit that commenced operation on or before
January 1, 2002. The new unit must be used for the same purpose as the replacement unit.”
Prop. at 37;
see
Statement at 28. In response to a question by IERG filed for the first hearing, the
Agency stated that, “[f]or the purpose of emissions averaging under this proposal, a replacement

59
unit must be
essentially
the same as the unit it replaces.” IERG Answers at 8 (emphasis added);
see
Tr.1 at 80-83. In its second motion to amend its rulemaking proposal, the Agency proposed
to replace its original language with a new subsection (a)(1)(C) clarifying the replacement units
that may be included in an averaging plan. The Agency explained that
[t]he new unit must be used for the same purpose and have substantially
equivalent or less process capacity or be permitted for less NO
x
emissions on an
annual basis than the actual NO
x
emissions of the unit or units that are replaced.
In addition, within 90 days after permanently shutting down a unit that is
replaced, the owner or operator of such unit must submit a written request to
withdraw or amend the applicable permit to reflect that the unit is no longer in
service before the replacement unit may be included in the emissions averaging
plan” Mot. Amend 2 at 3, 8-9.
Proposed subsection (a)(2) described units that may not be included in an emissions
averaging plan. Statement at 27;
see
Prop. at 37. First, under proposed subsection (a)(2)(A), a
plan may not include “[u]nits that commence operation after January 1, 2002, except as provided
by subsection (a)(1)(C) of this Section.” Prop. at 38;
see
Statement at 28,
supra
(discussing
subsection (a)(1)(C)). Under proposed subsection (a)(2)(B), a plan may not include “[u]nits that
the owner or operator is claiming are exempt pursuant to Section 217.162, 217.182, 217.202,
217.222, 217.242, or 217.432 of this Part, as applicable.” Prop. at 38;
see
Statement at 28. Also,
under proposed subsection (a)(2)(C), the Agency originally proposed that plans may not include
“[u]nits that are required to meet emission limits for NO
x
as provided for in an enforceable order,
unless such order specifically provides for operation pursuant to an emissions averaging plan.”
Prop. at 28;
see
Statement at 28. In its second motion to amend its rulemaking proposal, the
Agency proposed to amend this subsection to provide that plans may not include
[u]nits that are required to meet emission limits or control requirements for NO
x
as provided for in an enforceable order, unless such order allows for emissions
averaging. Nothing in this subparagraph (C) is intended to prohibit a petroleum
refinery from including industrial boilers or process heaters, or both, in an
emissions averaging plan where an enforceable order does not prohibit the
reductions made under such order from also being used for compliance with any
rules or regulations designed to address regional haze or the non-attainment status
of any area. Mot. Amend 2 at 3, 9.
In its first notice comments, the Agency proposed to amend subsection (a)(2)(C) as
follows:
[u]nits that are required to meet emission limits or control requirements for NO
x
as provided for in an enforceable order, unless such order allows for emissions
averaging. In the case of petroleum refineries, this subsection does not prohibit
including industrial boilers or process heaters, or both, in an emissions averaging
plan where an enforceable order does not prohibit the reductions made under such
order from also being used for compliance with any rules or regulations designed
to address regional haze or the non-attainment status of any area. PC 17 at 3.

60
Proposed subsection (b) provided that
an owner or operator must submit an emissions averaging plan to the Agency by
May 1, 2010, and such plan must include, but is not limited to, the list of affected
units included in the plan by unit identification number and a sample calculation
demonstrating compliance using the methodology provided in subsection (f) of
this Section for the ozone season (May 1 through September 30) and calendar
year (January 1 through December 31). Statement at 28;
see
Prop. at 38.
In its first motion to amend its rulemaking proposal, the Agency sought to extend the deadline to
submit an averaging plan to the Agency to January 1, 2012. Mot. Amend 1 at 6. In a question
filed for the first hearing on October 14, 2008, Midwest Generation asked whether a source may
decide after the deadline for submitting a plan that it wishes to perform averaging. MG
Questions at 3. The Agency responded that “[a]veraging plans can be amended once per year at
the discretion of the owner/operator.” MG Answers at 4. The Agency elaborated that a unit that
had not submitted an averaging plan before the initial deadline can be included in averaging at a
later date.
Id
.
Subsection (c), as originally proposed by the Agency, provided in its entirety that “[a]n
owner or operator may amend an emission plan only once per calendar year. Such an amended
plan must be submitted to the Agency by May 1 of the applicable calendar year. If an amended
plan is not received by the Agency by May 1 of the applicable calendar year, the previous year’s
plan will be the applicable emissions averaging plan.” Prop. at 38;
see
Statement at 28. In its
first motion to amend its rulemaking proposal, the Agency proposed to amend this subsection by
changing the May 1 submission deadlines to January 1. Mot. Amend 1 at 6.
Proposed subsection (d) provided that, notwithstanding subsection (c),
1)
If a unit that is listed in an emissions averaging plan is taken out of
service, the owner or operator must submit to the Agency, within 30 days
of such occurrence, an updated emissions averaging plan; or
2)
If a unit that is exempt from the requirements of Subpart E, F, G, H, I, or
M, as applicable, no longer qualifies for an exemption, the owner or
operator may amend its existing averaging plan to include such unit within
30 days of the unit no longer qualifying for the exemption.
See
Statement
at 28-29; Prop. at 38-39.
Proposed subsection (e) provided that the owner or operator must demonstrate
compliance for both the ozone season and the calendar year by using the methodology and the
units included in the most recent averaging plan submitted to the Agency, “the higher of the
monitoring data or test data determined pursuant to Section 217.157,” and “the actual hours of
operation for the applicable averaging plan period.” Statement at 29;
see
Prop. at 39. The
proposed subsection also provided that the owner or operator must “submit to the Agency by

61
March 1 following each calendar year, a compliance report containing the information required
by Section 217.156(i).” Statement at 29;
see
Prop. at 39.
Proposed subsection (f) “provides that the total mass of actual NO
x
emissions from the
units listed in the emissions averaging plan must be equal to or less than the total mass of
allowable NO
x
emissions for those units for both the ozone season and calendar year.”
Statement at 29;
see
Prop. at 39. The proposed subsection also includes the equation with which
to determine compliance. Prop. at 39-41.
Proposed subsection (g) provided that
the owner or operator of an emission unit subject to Subpart Q of this Part that is
located in either one of the areas set forth under Section 217.150(a)(1)(A) or (B)
of this Subpart that is complying through an emissions averaging plan under this
Section must comply with the applicable provisions for determining actual and
allowable emissions under Section 217.390 of Subpart Q, the testing and
monitoring requirements under Section 217.394 of Subpart Q, and the
recordkeeping and reporting requirements under Section 217.396 of Subpart Q.
Statement at 29;
see
Prop. at 41.
In its first notice comments, the Agency proposed to correct the reference to “Section
217.150(a)(1)(A) or (B)” to read as “Section 217.150(a)(1)(A)(i) or (ii).” PC 17 at 3;
see
33 Ill.
Reg. 6941 (May 22, 2009) (reorganizing proposed Section 217.150).
In its second motion to amend its rulemaking proposal, the Agency sought to add a
subsection (h). Mot. Amend 2 at 3-4, 9. That proposed new subsection provides in its entirety
that
[t]he owner or operator of an emission unit located at a petroleum refinery who is
demonstrating compliance with an applicable Subpart through an emissions
averaging plan under this Section may exclude from the calculation demonstrating
compliance those time periods when an emission unit included in the emissions
averaging plan is shut down for a maintenance turnaround, provided that such
owner or operator notify the Agency in writing at least 30 days in advance of the
shutdown of the emission unit for the maintenance turnaround and the shutdown
of the emission unit does not exceed 45 days per ozone season or calendar year
and NO
x
pollution control equipment, if any, continues to operate on all other
emission units operating during the maintenance turnaround. Mot. Amend 2 at 9.
Also in its second motion to amend its rulemaking proposal, the Agency sought to add a
subsection (i). Mot. Amend 2 at 4, 9. That proposed new subsection provides in its entirety that
[t]he owner or operator of an emission unit that combusts a combination of coke
oven gas and other gaseous fuels and located at a source that manufactures iron
and steel who is demonstrating compliance with an applicable Subpart through
an emissions averaging plan under this Section may exclude from the calculation

62
demonstrating compliance those time periods when the coke oven gas
desulfurization unit included in the emissions averaging plan is shut down for
maintenance, provided that such owner or operator notify the Agency in writing
at least 30 days in advance of the shutdown of the coke oven gas desulfurization
unit for maintenance and such shutdown does not exceed 35 days per ozone
season or calendar year and NO
x
pollution control equipment, if any, continues
to operate on all other emission units operating during the maintenance period.
Mot. Amend 2 at 9.
In its first notice comments, the Agency proposed to add a subsection (j) reading as
follows:
[t]he owner or operator of an emission unit located at a petroleum refinery who is
demonstrating compliance with an applicable Subpart through an emissions
averaging plan under this Section may exclude from the calculation
demonstrating compliance those time periods when NO
x
pollution control
equipment that controls one or more emission units included in the emissions
averaging plan is shut down for a maintenance turnaround, provided that such
owner or operator notify the Agency in writing at least 30 days in advance of the
shutdown of the NO
x
pollution control equipment for the maintenance
turnaround and the shutdown of the NO
x
pollution control equipment does not
exceed 45 days per ozone season or calendar year, and except for those emission
units vented to the NO
x
pollution control equipment undergoing the maintenance
turnaround, NO
x
pollution control equipment, if any, continues to operate on all
other emission units operating during the maintenance turnaround. PC 17 at 3.
Subpart E: Industrial Boilers
Section 217.160: Applicability.
The Agency sought to add a new section addressing
applicability of its proposal to industrial boilers. Prop. at 41-42. Proposed subsection (a)
provided that “the provisions of Subparts C and D apply to all industrial boilers located at
sources subject to Subpart D pursuant to Section 217.150.” Statement at 30;
see
Prop. at 42;
see
also supra
at 44-46 (addressing applicability of general requirements). The Agency stated that
there are 12 industrial boilers subject to the NO
x
SIP Call affected by this proposal and an
additional 68 industrial boilers less than 250 mmBtu that are not subject to the NO
x
SIP Call.
TSD at 130, Statement at 10;
see
MG Answers at 8.
In a question filed for the first hearing on October 14, 2008, Midwest Generation claimed
that “[t]he ‘all industrial boilers’ language in Section 217.160(a) and similar language in the
other subparts could be construed to expand the scope of Section 217.150(a)(2), which refers to
‘any industrial boiler [and other types of emission units] that emits NO
x
in an amount equal to or
greater than 15 tons per year and equal to or greater than five tons per ozone season.” MG
Questions at 2;
see
Prop. at 41-42. Midwest Generation questions whether the Agency intends
“to expand the applicability of the rule in this way.” MG Questions at 2. The Agency responds
by expressing the intent “that each Subpart apply to all of the affected emission units at an
affected source,
e.g.
, ‘any’ emission unit that meets the applicability criteria.” MG Answers at 3.

63
Proposed subsection (b) provided that “the provisions of Subpart D do not apply to
boilers serving a generator that has a nameplate capacity of 25 MWe or less and produces
electricity for sale, and cogeneration units, as that term is defined in Section 225.130 of Part 225,
if such boilers or cogeneration units are subject to the CAIR NO
x
Trading Programs under
Subpart D or E of Part 225.” Statement at 30;
see
Prop. at 42.
In a question filed for the first hearing on October 14, 2008, Midwest Generation stated
that, “[b]ased upon the proposed applicability language in Subpart M, Section 217.340, [and]
assuming the D.C. Circuit Court issues the mandate implementing its decision in the appeal of
the CAIR, EGUs would be subject to the provisions of Subpart D.” MG Questions at 3-4.
Midwest Generation consequently asked whether the Agency would consider amending
subsection (b) as follows: “[t]he provisions of this Subpart do not apply to boilers serving a
generator that has a nameplate capacity greater than 25 MWe and produces electricity for sale,
and cogeneration units, as that term is defined in Section 225.230 of Part 225, if such boilers or
cogeneration units are subject to the CAIR NO
x
Trading Programs under Subpart D or E of Part
225.”
Id.
at 4.
Responding to Midwest Generation, the Agency stated that it was “amenable” to
amending its proposed definition in the following fashion: “[t]he provisions of this Subpart do
not apply to boilers serving a generator that has a nameplate capacity greater than 25 MWe and
produces electricity for sale, and cogeneration units, as that term is defined in Section 225.130 of
Part 225, if such boilers or cogeneration units are subject to meet the applicability criteria under
Subpart M of Part 217 the CAIR NO
x
Trading Programs under Subpart D or E of Part 225. MG
Answers at 4-6.
In its first motion to amend its rulemaking proposal, the Agency recommended that the
Board “[a]mend Section 217.160 by amending subsection (b) to reflect the provisions as
previously agreed to between the Illinois EPA and Midwest Generation as reflected in the Illinois
EPA’s Answers to Midwest Generation’s Questions for Agency Witnesses, filed September 30,
2008, and the October 14, 2008, hearing.” Mot. Amend 1 at 6;
see
MG Question at 3-4, MG
Answers at 4-6.
In its post-hearing comments, Midwest Generation stated that,
[w]ith the amendments proposed to the Board by the Agency in its Motion to
Amend Rulemaking Proposal ("Agency's Motion") filed January 30, 2009,
Midwest Generation generally supports the Agency's proposal as it applies to
electric generating units ("EGUs"). The proposed amendments incorporate by
reference provisions agreed to between the Agency and Midwest Generation as
part of the Agency's Answers to Midwest Generation's Questions for Agency
Witnesses ("Agency's Answers"), which were filed before this Board on
September 30, 2008. PC 9 at 1-2 (noting Agency’s proposed amendment of
Section 217.160);
see
Mot. Amend 1 at 6, Tr.1 at 199-200.

64
In its first notice comments, the Agency proposed to amend subsection (b) “by
striking the references to ‘cogeneration units’ and adding reference to boilers that ‘meet
the applicability criteria under Subpart M of Part 217.’” PC 17 at 4, citing In the Matter
of: Nitrogen Oxides Emissions from Various Source Categories: Amendments to 35 Ill.
Adm. Code Parts 211 and 217, R08-19, slip op. at 45-46 (May 7, 2009). Specifically, the
Agency proposed language providing that “[t]he provisions of this Subpart do not apply
to boilers serving a generator that has a nameplate capacity greater than 25 MWe and
produces electricity for sale, if such boilers meet the applicability criteria under Subpart
M of Part 217.” PC 17 at 4.
Proposed subsection (c) provided that “the provisions of Subpart D do not apply to
fluidized catalytic cracking units, their regenerator and associated CO boiler or boilers and CO
furnace or furnaces where present, that commenced operation prior to January 1, 2008, if such
units are located at a petroleum refinery and such units are required to meet emission limits for
NO
x
as provided for in an enforceable order.” Statement at 30-31;
see
Prop. at 42.
In its first motion to amend its rulemaking proposal, the Agency sought to amend
subsection (c) to provide that
[t]he provisions of this Subpart do not apply to fluidized catalytic cracking units,
their regenerator and associated CO boiler or boilers and CO furnace or furnaces
where present, that commenced operation prior to January 1, 2008, if such units
are located at a petroleum refinery and such units are required to meet emission
limits or control requirements for NO
x
as provided for in an enforceable order.
Mot. Amend 1 at 6
In its second motion to amend, the Agency proposed to remove the January 1, 2008, date for
commencement of operation “in the non-applicability provisions pertaining to certain fluidized
bed catalytic cracking units located at a petroleum refinery.” Mot. Amend 2 at 5, 9-10.
Section 217.162: Exemptions.
The Agency proposed to add a new section addressing
exemptions, which provides in its entirety that, “[n]otwithstanding Section 217.160 of this
Subpart, the provisions of this Subpart do not apply to an industrial boiler operating under a
federally enforceable limit of NO
x
emissions from such boiler to less than 15 tons per year and
less than five tons per ozone season.” Prop. at 42;
see
Statement at 31, Kaleel Pre-filed Test. at
3.
Section 217.164: Emissions Limitations.
The Agency proposed to add a new section
addressing emission limitations from industrial boilers. Statement at 31; Prop. at 42-43;
see
generally
TSD at 5-44 (Industrial Boilers and Electric Generating Unit Boilers). Originally, the
Agency proposed that, “[o]n and after May 1, 2010, no person shall cause or allow emissions of
NO
x
into the atmosphere from any industrial boiler to exceed the limitations set forth under this
Section.” Statement at 31;
see
Prop. at 42-43. The Agency proposed specific limitations or
requirements based first on the unit’s fuel and then on its rated heat input capacity. Prop. at 42-
43 (proposed subsections (a) through (d)). The Agency also proposed that “[c]ompliance must

65
be demonstrated with the applicable emissions limitations on an ozone season and annual basis.”
Prop. at 42;
see
Statement at 31.
In its first motion to amend its rulemaking proposal, the Agency proposed to amend the
first sentence of Section 217.164 by extending the compliance deadline to January 1, 2012. Mot.
Amend 1 at 6. In its first notice comment, the Agency proposed to amend the first paragraph of
Section 217.164 to read as follows:
[e]xcept as provided for under Section 217.152, on and after January 1, 2012, no
person shall cause or allow emissions of NO
x
into the atmosphere from any
industrial boiler to exceed the following limitations. Compliance must be
demonstrated with the applicable emissions limitations on an ozone season and
annual basis. PC 17 at 4.
In a question filed for the first hearing on October 14, 2008, Midwest Generation asked
the Agency to state the “basis for establishing a rate of 0.008 lb/mmBtu rate for gas-fired
industrial boilers greater than 100 mmBtu.” MG Questions at 3. The Agency responded that its
TSD establishes this basis. MG Answers at 4, citing TSD at 43 (Table 2-17a: Cost Effectiveness
Data for Natural Gas-Fired ICI Boilers).
In testimony on behalf of U.S. Steel for the second hearing, Mr. Siebenberger stated that
the Agency’s proposed emission limit of 0.08 lbs/MMBtu for industrial boilers greater than 100
MMBtu/hr relying on natural gas or other gaseous fuels does not take into account the “unique
characteristics” of specific U.S. Steel boilers. Exh. 10 at 6. Those unique characteristics
“include the combustion of a varying fuel mix of desulfurized or non-desulfurized coke oven gas
in combination with blast furnace gas and natural gas.”
Id
. U.S Steel proposed alternate
emissions limits both for its Boilers 11 and 12 and for its reheat furnaces.
Id
. at 6, 7;
see
Tr.1 at
102-03 (addressing Agency consideration of coke oven gas fuel).
In testimony filed on behalf of IERG for the second hearing, Mr. Kolaz argued that the
difference in emissions between the Agency’s original proposal and IERG’s alternate proposal is
“relatively small.” Exh. 6 at 22. Mr. Kolaz further argued that IERG’s proposed emission limit
of 0.12 lbs/mmBtu for industrial boilers greater than 100 MMBtu/hr relying on natural gas or
other gaseous fuels is “more practically achievable.”
Id
. at 23;
see id
. at Exhs. 1, 2. Mr. Kolaz
also questioned the Agency’s proposed compliance date on grounds including the practical
ability of sources to implement these requirements.
Id.
at 12-15.
In testimony filed on behalf of ConocoPhillips for the second hearing, Mr. Dunn stated
that the Agency’s proposed emission limit of 0.08 lb/MMBtu for industrial boilers greater than
100 MMBtu/hr relying on natural gas or other gaseous fuels is “overly stringent.” Exh. 9 at 6.
ConocoPhillips recommended an emission limit of 0.12 lb/MMBtu, as recommended by IERG.
Id
. at 9. ConocoPhillips further argued that the Agency’s compliance deadline is “not
achievable.”
Id
.
In post-hearing comments filed January 20, 2009, ConocoPhillips again addressed the
emission limitation of 0.08 lb/mmBtu for gas-fired boilers greater than 100 mmBtu/hr. PC 5 at

66
3-4. ConocoPhillips argued that the proposed limit “is overly stringent for typical industrial
boilers when burning refinery fuel gas” and “does not adequately consider the economic
consequences” of installing the controls that comply with it.
Id
. at 3-4.
In the second motion to amend, the Agency proposed to change the emissions limitation
for an industrial boiler, circulating fluidized bed combustor, with a rated heat input capacity
greater than 100 mmBtu/hr from 0.10 lb/mmBtu to 0.12 lb/mmBtu. Mot. Amend 2 at 4. The
Agency states that, “[d]uring discussions with affected parties, emissions information from an
existing source with such a unit was provided to Illinois EPA, and such information necessitated
a modification of the emissions limitation.”
Id
. at 4, 10. Also in the second motion to amend,
the Agency proposed to add in a new subsection (e) a formula establishing “an emissions
limitation to be calculated for an industrial boiler combusting a combination of natural gas, coke
oven gas, and blast furnace gas under Subpart D.”
Id
. at 4, 11.
In its first notice comments, the Agency proposed a correction to the equation in
subsection (e). PC 17 at 4, citing In the Matter of: Nitrogen Oxides Emissions from Various
Source Categories: Amendments to 35 Ill. Adm. Code Parts 211 and 217, R08-19, slip op. at 98
(May 7, 2009);
see also
PC 19 at 6 (proposing correction in U.S. Steel first notice comments).
Section 217.165: Combination of Fuels.
The Agency proposed to add a new section
addressing combination of fuels, which provides in its entirety that “[t]he owner or operator of an
industrial boiler subject to this Subpart and operated with any combination of fuels must comply
with a heat input weighted average emissions limitation to demonstrate compliance with Section
217.164 of this Subpart.” Prop. at 43;
see
Statement at 31;
see also supra
at 64-66 (discussing
proposed Section 217.164).
Section 217.166: Methods and Procedures for Combustion Tuning.
The Agency
proposed to add a new section addressing combustion tuning. Prop. at 44. The proposed section
first provided that “the owner or operator of an industrial boiler subject to the combustion tuning
requirements of Section 217.164 must have combustion tuning performed at least annually.”
Statement at 31;
see
Prop. at 44. It also provided that “the combustion tuning must be performed
by an employee of the owner or operator or a contractor who has successfully completed a
training course on the combustion tuning of boilers firing the fuel or fuels that are fired in the
boiler.” Statement at 31;
see
Prop. at 44. Finally, the proposed section also sought to require
that the owner or operator maintain combustion tuning records containing five specific items and
make those records available to the Agency upon request. Statement at 31-32;
see
Prop. at 44
(proposed subsections (1) through (5)).
Subpart F: Process Heaters
Section 217.180: Applicability.
The Agency proposed to add a section addressing
applicability and providing in its entirety that “[t]he provisions of Subpart C of this Part and this
Subpart apply to all process heaters located at sources subject to this Subpart pursuant to Section
217.150 of this Part.” Prop. at 44;
see
Statement at 32,
supra
at 44-46 (discussing Section
217.150);
see generally
TSD at 46-65 (Process Heaters).

67
In a question filed for the first hearing on October 14, 2008, Midwest Generation
suggested that the “all process heaters” language in Section 217.160(a) could be construed to
expand the scope of Section 217.150(a)(2), which refers to “any . . . process heater . . . that emits
NO
x
in an amount equal to or greater than 15 tons per year and equal to or greater than five tons
per ozone season.” MG Questions at 2;
see
Prop. at 26 (proposed Section 217.150(a)(2)).
Midwest Generation questioned whether the Agency intended “to expand the applicability of the
rule in this way.” MG Questions at 2. The Agency responded by expressing the intent “that
each Subpart apply to all of the affected emission units at an affected source,
e.g.
, ‘any’ emission
unit that meets the applicability criteria.” MG Answers at 3.
Section 217.182: Exemptions.
The Agency proposed to add a section addressing
exemptions and providing in its entirety that, “[n]otwithstanding Section 217.180 of this Section,
the provisions of this Subpart do not apply to a process heater operating under a federally
enforceable limit of NO
x
emissions from such heater to less than 15 tons per year and less than
five tons per ozone season.” Prop. at 45;
see
Statement at 33, Kaleel Pre-filed Test. at 3.
In testimony filed on behalf of IERG for the second hearing, Mr. Kolaz stated that “most
of the process heaters affected by this rule are located at petroleum refineries,” which “cannot
make changes to their process heaters without planning the work to occur during maintenance
turnarounds.” Exh. 6. at 23. He further stated that “it appears that the Agency used the emission
reductions from the USEPA refinery consent decrees for the attainment modeling conducted by
LADCO.”
Id
. at 24. He proposed that “the Agency consider the reductions from the federally
enforceable consent decrees to constitute RACT for these facilities.”
Id
. He identified this
section as language that might be modified to adopt this proposed amendment.
Id
.
Section 217.184: Emissions Limitations.
The Agency proposed to add a new section
addressing emission limitations from process heaters. Statement at 33; Prop. at 45-46;
see
generally
TSD at 46-65 (Process Heaters). Originally, the Agency proposed that, “[o]n and after
May 1, 2010, no person shall cause or allow emissions of NO
x
into the atmosphere from any
process heater” to exceed specified limitations. Prop. at 45;
see
Statement at 33. The Agency
proposed specific limitations or requirements based first on the unit’s fuel and then on its rated
heat input capacity in mmBtu/hr. Prop. at 45-46 (proposed subsections (a), (b), and (c)). The
Agency also proposed that “[c]ompliance must be demonstrated with the applicable emissions
limitations on an ozone season and annual basis.” Prop. at 45;
see
Statement at 33.
In its first motion to amend its rulemaking proposal, the Agency proposed to amend the
first sentence of Section 217.184 by extending the compliance deadline to January 1, 2012. Mot.
Amend 1 at 7. In its first notice comments, the Agency proposed to amend the first paragraph of
Section 217.184 to read as follows:
[e]xcept as provided for under Section 217.152, on and after January 1, 2012, no
person shall cause or allow emissions of NO
x
into the atmosphere from any
process heater to exceed the following limitations. Compliance must be
demonstrated with the applicable emissions limitations on an ozone season and
annual basis. PC 17 at 4.

68
In testimony filed on behalf of ConocoPhillips for the second hearing, Mr. Dunn stated
that the Agency’s proposed emission limit of 0.07 lb/MMBtu for process heaters greater than
100 MMBtu/hr relying on gaseous fuels is “too stringent for typical process heaters” and requires
“control technology that is well beyond RACT.” Exh. 9 at 9. He further stated that
ConocoPhillips “agrees with IERG’s suggestions that the NO
x
emission limit of process heaters
be set at 0.12 lb NO
x
/MMBtu.”
Id
. at 12. ConocoPhillips further argued that the Agency’s
compliance deadline is “not achievable.”
Id
.
In the second motion to amend, the Agency proposed to amend “the emissions limitation
for a process heater with a rated heat input capacity greater than 100 mmBtu/hr combusting
natural gas or other gaseous fuels” from 0.07 lb/mmBtu to 0.08 lb/mmBtu. Mot. Amend 2 at 5,
11-12.
Section 217.185: Combination of Fuels.
The Agency proposed to add a new section
addressing combination of fuels, which provides in its entirety that “[t]he owner or operator of a
process heater subject to this Subpart and operated with any combination of fuels must comply
with a heat input weighted average emissions limitation to demonstrate compliance with Section
217.184 of this Subpart.” Prop. at 46;
see
Statement at 33;
see also supra
at 67-68 (discussing
proposed Section 217.184).
Section 217.186: Methods and Procedures for Combustion Tuning.
The Agency
proposed to add a new section addressing combustion tuning of process heaters. Prop. at 46-47.
The proposed section first provided that “the owner or operator of a process heater subject to the
combustion tuning requirements of Section 217.184 must have combustion tuning performed on
the heater at least annually.” Statement at 33;
see
Prop. at 44. The proposed section also
provided that “[t]he combustion tuning must be performed by an employee of the owner or
operator or a contractor who has successfully completed a training course on the combustion
tuning of heaters firing the fuel or fuels that are fired in the heater.” Statement at 33;
see
Prop. at
46. Finally, the proposed section also sought to require that the owner or operator maintain
combustion tuning records containing five specific items and make those records available to the
Agency upon request. Statement at 33-34;
see
Prop. at 46 (proposed subsections (1) through
(5)).
Subpart G: Glass Melting Furnaces
Section 217.200: Applicability.
The Agency proposed to add a section addressing
applicability and providing in its entirety that “[t]he provisions of Subpart C of this Part and this
Subpart apply to all glass melting furnaces located at sources subject to this Subpart pursuant to
Section 217.150 of this Part.” Prop. at 47;
see
Statement at 34,
supra
at 44-46 (discussing
Section 217.150);
see generally
TSD at 102-17 (Glass Melting Furnaces).
In a question filed for the first hearing on October 14, 2008, Midwest Generation
suggested that the “all glass melting furnaces” language in Section 217.200 could be construed to
expand the scope of Section 217.150(a)(2), which refers to “any . . . glass melting furnace . . .
that emits NO
x
in an amount equal to or greater than 15 tons per year and equal to or greater than
five tons per ozone season.” MG Questions at 2;
see
Prop. at 26 (proposed Section

69
217.150(a)(2)). Midwest Generation questioned whether the Agency intended “to expand the
applicability of the rule in this way.” MG Questions at 2. The Agency responded by expressing
the intent “that each Subpart apply to all of the affected emission units at an affected source,
e.g.
,
‘any’ emission unit that meets the applicability criteria.” MG Answers at 3.
Section 217.202: Exemptions.
The Agency proposed to add a section addressing
exemptions and providing in its entirety that, “[n]otwithstanding Section 217.200 of this Section,
the provisions of this Subpart do not apply to a glass melting furnace operating under a federally
enforceable limit of NO
x
emissions from such furnace to less than 15 tons per year and less than
five tons per ozone season.” Prop. at 47;
see
Statement at 35, Kaleel Pre-filed Test. at 3.
In a post-hearing comment filed November 25, 2008, Saint-Gobain expressed the belief
that “a narrow exception should be made to the May 1, 2010 compliance date for entities that
enter into an enforceable agreement with IEPA to install control technology that can achieve
NO
x
emission rates significantly below the 5.0 lbs/ton limit pursuant to an enforceable schedule
extending beyond 2010. PC 2 at 1. As Saint-Gobain was negotiating such an agreement, it
proposed the following addition to this exemptions section:
[n]otwithstanding the compliance date set forth in Section 217.155(b) and
217.204, a compliance date of December 31 2014, shall apply when the owner or
operator of a container glass melting furnace subject to Subpart F has executed a
binding and enforceable agreement by December 31, 2009 with the State of
Illinois that requires compliance with a NO
x
limit that is less than 30 percent of
the emission limit in Section 217.204.
Id
.;
but see
Mot. Amend. 1 at 3
(incorporating substance of proposed language into Section 217.152(b)).
Section 217.204: Emissions Limitations.
The Agency proposed to add a new section
addressing emission limitations for glass melting furnaces. Statement at 35; Prop. at 47;
see
generally
TSD at 102-17 (Glass Melting Furnaces). Originally, the Agency proposed that, “[o]n
and after May 1, 2010, no person shall cause or allow emissions of NO
x
into the atmosphere
from any glass melting furnace” to exceed specified limitations. Prop. at 47;
see
Statement at 35.
The Agency proposed specific limitations based on the unit’s product type as container glass, flat
glass, or other glass. Prop. at 47 (proposed subsections (a), (b), and (c)). The Agency also
proposed that “[c]ompliance must be demonstrated with the emissions limitations on an ozone
season and annual basis.” Prop. at 47;
see
Statement at 35.
In a post-hearing comment filed November 25, 2008, Saint-Gobain expressed the belief
that “a narrow exception should be made to the May 1, 2010 compliance date for entities that
enter into an enforceable agreement with IEPA to install control technology that can achieve
NO
x
emission rates significantly below the 5.0 lbs/ton limit pursuant to an enforceable schedule
extending beyond 2010. PC 2 at 1. Noting that it was negotiating such an agreement, Saint-
Gobain argued that it “cannot afford to install the technology required to meet an interim limit of
5.0 lb/ton for the period between the compliance date under Section 217.204 and the anticipated
schedule for installation of alternative technology at the end of 2014.”
Id
.;
see
Tr.2 at 13-16
(addressing negotiation of consent decree). Saint-Gobain also referred to the cost of installing
CEMS devices.
See
PC 2 at 1-2.

70
In a pre-hearing comment filed January 20, 2009, Saint-Gobain proposed to add to
Section 217.202 language providing that “Section 217.204 shall not apply during glass furnace
startup (not to exceed 70 days) or idling (operation at less than 35% of furnace capacity).” PC 4
at 2. Saint-Gobain also proposed a formula with which to determine a NO
x
emission limit
applicable to those startup and idling periods.
See id
.
In its first motion to amend its rulemaking proposal, the Agency proposed to amend the
first sentence of Section 217.204 by extending the compliance deadline to January 1, 2012. Mot.
Amend 1 at 7. The Agency also proposed to add a subsection providing in part that “[t]he
emissions limitations under this Section do not apply during glass melting furnace startup (not to
exceed 70 days) or idling (operation at less than 35% of furnace capacity).”
Id
. The Agency’s
proposed new subsection also included a formula for determining NO
x
emissions limitations
during startup and idle periods.
Id
.
In its first notice comments, the Agency proposed, “due to the special characteristics of
glass melting furnaces and further discussions with Saint-Gobain Containers, Inc.” to amend
subsection (b) as follows:
[t]he emissions during glass melting furnace startup (not to exceed 70 days) or
furnace idling (operation at less than 35% of furnace capacity) shall be excluded
from calculations for the purpose of demonstrating compliance with the seasonal
and annual emissions limitations under this Section, provided that such owner or
operator, at all times, including periods of startup and idling, to the extent
practicable, maintain and operate any affected emission unit including associated
air pollution control equipment in a manner consistent with good air pollution
control practice for minimizing emissions. The owner or operator of a glass
melting furnace must maintain records that include the date, time, and duration of
any startup or idling in the operation of such glass melting furnace. PC 17 at 4-5.
Subpart H: Cement and Lime Kilns
Section 217.220: Applicability.
The Agency proposed to add a section addressing
applicability to cement and lime kilns. Prop. at 48;
see
Statement at 35-36. Proposed subsection
(a) provided in its entirety that, “[n]otwithstanding Subpart T of this Part, the provisions of
Subpart C of this Part and this Subpart apply to all cement kilns located at sources subject to this
Subpart pursuant to Section 217.150 of this Part.” Prop. at 48;
see
Statement at 35-36;
supra
at
44-46 (discussing Section 217.150);
see generally
TSD at 66-85 (Cement Kilns). Proposed
subsection (b) provided in its entirety that “[t]he provisions of Subpart C of this Part and this
Subpart apply to all lime kilns located at sources subject to this Subpart pursuant to Section
217.150 of this Part. Prop. at 48;
see
Statement at 35-36;
see supra
at 44-46 (discussing Section
217.150);
see generally
TSD at 86-91 (Lime Kilns).
In a question filed for the first hearing on October 14, 2008, Midwest Generation
suggested that the “all cement kilns” and “all lime kilns” language in Section 217.220 could be
construed to expand the scope of Section 217.150(a)(2), which refers to “any . . . cement kiln [or]

71
lime kiln . . . that emits NO
x
in an amount equal to or greater than 15 tons per year and equal to
or greater than five tons per ozone season.” MG Questions at 2;
see
Prop. at 26 (proposed
Section 217.150(a)(2)). Midwest Generation questioned whether the Agency intended “to
expand the applicability of the rule in this way.” MG Questions at 2. The Agency responded by
expressing the intent “that each Subpart apply to all of the affected emission units at an affected
source,
e.g.
, ‘any’ emission unit that meets the applicability criteria.” MG Answers at 3.
In another question filed for the first hearing on October 14, 2008, Midwest Generation
asked why, if there are no cement kilns in the nonattainment areas, cement kilns are included in
the rulemaking. MG Questions at 1;
see also
IERG Questions at 4. The Agency responded by
stating that “[t]here are no cement kilns in the current NAAs, although there is a cement kiln in
Massac County, which USEPA intends to designate as nonattainment for the 24-hour PM
2.5
NAAQS.” MG Answers at 2, citing
id
., Attachment 1 (USEPA review of air quality
designations);
see also
IERG Answers at 6, citing TSD at 66 (noting that none of eight Illinois
cement kilns are situated in nonattainment areas), Tr.1 at 57-62.
In his testimony on behalf of the Agency at the first hearing on October 14, 2008, Mr.
Kaleel noted that the Agency had initially drafted these proposed regulations to have statewide
applicability and that there are cement kilns situated in the state’s attainment areas. Tr.1 at 61.
He also noted that, under the revised ozone and PM
2.5
standards, “there may be some
adjustments necessary to the non-attainment areas.”
Id
. Mr. Kaleel also argued that the Agency
has already performed the engineering and cost analysis in support of these proposed rules.
Id
. at
62. Although he acknowledged that a change in the boundaries of the nonattainment areas would
require changing the regulation, including cement kilns “would send a clear message to units that
potentially become non-attainment in the future that they would know what their target is, what it
is they have to meet.”
Id
.
In testimony filed on behalf of IERG for the second hearing on December 9, 2008, Mr.
Kolaz argued that, because no cement kilns exist in the nonattainment areas, cement kilns should
not be included in the Agency’s proposed regulations. Exh. 6 at 19, 24. He further argued that
“[a]ny new facility with such a unit in the applicable areas would be subject to controls stricter
than RACT.”
Id
. at 19. He also argued that, “[i]f new nonattainment areas are identified in
Illinois, this proposed rule would need to be amended to incorporate those areas if NO
x
reductions are deemed necessary and appropriate to address the air quality conditions.”
Id
.;
see
Tr.1 at 57-60.
Section 217.222: Exemptions.
The Agency proposed to add a section addressing
exemptions and providing in its entirety that, “[n]otwithstanding Section 217.220 of this Subpart,
the provisions of this Subpart do not apply to a cement kiln or lime kiln operating under a
federally enforceable limit of NO
x
emissions from such kiln to less than 15 tons per year and less
than five tons per ozone season.” Prop. at 48;
see
Statement at 36, Kaleel Pre-filed Test. at 3.
Section 217.224: Emissions Limitations.
The Agency proposed to add a new section
addressing emission limitations from cement kilns and lime kilns. Statement at 36; Prop. at 48-
49. Originally, the Agency proposed in subsection (a) that, “[o]n and after May 1, 2010, no
person shall cause or allow emissions of NO
x
into the atmosphere from any cement kiln” to

72
exceed specified limitations. Prop. at 48;
see
Statement at 36. The Agency proposed specific
limitations based on the unit’s type. Prop. at 48 (proposed subsections (a)(1) through (a)(4)).
The Agency also proposed in subsection (b) that, “[o]n and after May 1, 2010, no person shall
cause or allow emissions of NO
x
into the atmosphere from any lime kiln” to exceed specified
limitations. Prop. at 49;
see
Statement at 36. The Agency also proposed that “[c]ompliance
must be demonstrated with the emissions limitations on an ozone season and annual basis.”
Prop. at 48;
see
Statement at 36.
In its first motion to amend its rulemaking proposal, the Agency proposed to amend the
first sentence of subsections (a) and (b) by extending the compliance deadline to January 1,
2012. Mot. Amend 1 at 8.
Subpart I: Iron and Steel and Aluminum Manufacturing
Section 217.240: Applicability.
The Agency proposed to add a section addressing
applicability to iron and steel and aluminum manufacturing. Prop. at 49;
see
Statement at 36-37.
Proposed subsection (a) provided in its entirety that “[t]he provisions of Subpart C of this Part
and this Subpart apply to all reheat furnaces, annealing furnaces, and galvanizing furnaces used
in iron and steel making located at sources subject to this Subpart pursuant to Section 217.150 of
this Part.” Prop. at 49;
see
Statement at 36-37;
supra
at 44-46 (discussing Section 217.150);
see
generally
TSD at 92-101 (Reheat, Annealing, and Galvanizing Furnaces at Iron/Steel plants).
Proposed subsection (b) provided in its entirety that “[t]he provisions of Subpart C of this Part
and this Subpart apply to all reverberatory furnaces and crucible furnaces used in aluminum
melting located at sources subject to this Subpart pursuant to Section 217.150 of this Part. Prop.
at 49;
see
Statement at 36-37;
see supra
at 44-46 (discussing Section 217.150);
see generally
TSD at 118-25 (Aluminum Melting Furnaces).
In a question filed for the first hearing on October 14, 2008, Midwest Generation
suggested that the “all reheat furnaces, annealing furnaces, and galvanizing furnaces used in iron
and steel making” and “all aluminum reverberatory furnaces and crucible furnaces used in
aluminum melting” language in Section 217.240 could be construed to expand the scope of
Section 217.150(a)(2), which refers to “any . . . iron and steel reheat, annealing, or galvanizing
furnace, [or] aluminum reverberatory or crucible furnace . . . that emits NO
x
in an amount equal
to or greater than 15 tons per year and equal to or greater than five tons per ozone season.” MG
Questions at 2;
see
Prop. at 26 (proposed Section 217.150(a)(2)). Midwest Generation
questioned whether the Agency intended “to expand the applicability of the rule in this way.”
MG Questions at 2. The Agency responded by expressing the intent “that each Subpart apply to
all of the affected emission units at an affected source,
e.g.
, ‘any’ emission unit that meets the
applicability criteria.” MG Answers at 3.
In another question filed for the first hearing on October 14, 2008, Midwest Generation
asked why, if there are no aluminum melting furnaces affected by the proposal, the rule includes
that sector. MG Questions at 1;
see also
IERG Questions at 4. The Agency responded by stating
that “[t]here is an aluminum melting furnace in the Chicago non-attainment area (NAA),
although it has not operated for several years. To the best of our knowledge, the emission unit

73
has not been torn down, so it is possible that the company, or a future owner, will seek to operate
the furnace in the future.” MG Answers at 1-2;
see
Tr.1 at 60-61;
see also
IERG Answers at 6.
In testimony filed on behalf of IERG for the second hearing on December 9, 2008, Mr.
Kolaz argued that, because no aluminum reverberatory or crucible furnaces exist in the
nonattainment areas, they should not be included in the Agency’s proposed regulations. Exh. 6
at 19, 24, citing Tr.1 at 60-61. He further argued that “[a]ny new facility with such a unit in the
applicable areas would be subject to controls stricter than RACT.” Exh. 6 at 19. He also argued
that, “[i]f new nonattainment areas are identified in Illinois, this proposed rule would need to be
amended to incorporate those areas if NO
x
reductions are deemed necessary and appropriate to
address the air quality conditions.”
Id
.;
see
Tr.1 at 57-60.
Section 217.242: Exemptions.
The Agency proposed to add a section addressing
exemptions and providing in its entirety that, “[n]otwithstanding Section 217.240 of this Subpart,
the provisions of this Subpart do not apply to an iron and steel reheat furnace, annealing furnace,
or galvanizing furnace, or aluminum reverberatory furnace or crucible furnace operating under a
federally enforceable limit of NO
x
emissions from such furnace to less than 15 tons per year and
less than five tons per ozone season.” Prop. at 49;
see
Statement at 36, Kaleel Pre-filed Test. at
3.
Section 217.244: Emissions Limitations.
The Agency proposed to add a new section
addressing emission limitations for iron and steel and aluminum manufacturing. Statement at
36-37; Prop. at 50-51. Originally, the Agency proposed in subsection (a) that, “[o]n and after
May 1, 2010, no person shall cause or allow emissions of NO
x
into the atmosphere from any
reheat furnace, annealing furnace, or galvanizing furnace use in iron and steel making” to exceed
specified limitations. Prop. at 50;
see
Statement at 37. The Agency proposed specific emissions
limitations based on the unit’s type. Prop. at 50 (proposed subsections (a)(1) through (a)(9)).
The Agency also proposed in subsection (b) that, “[o]n and after May 1, 2010, no person shall
cause or allow emissions of NO
x
into the atmosphere from any reverberatory furnace or crucible
furnace used in aluminum melting” to exceed specified limitations. Prop. at 50;
see
Statement at
37. The Agency also proposed with regard to both subsections that “[c]ompliance must be
demonstrated with the emissions limitations on an ozone season and annual basis.” Prop. at 50;
see
Statement at 37.
In its first motion to amend its rulemaking proposal, the Agency proposed to amend the
first sentence of subsections (a) and (b) by extending the compliance deadline to January 1,
2012. Mot. Amend 1 at 8-9. In its second motion to amend the proposal, the Agency proposed
to change the emissions limitation for a recuperative reheat furnace combusting natural gas from
0.05 lb/mmBtu to 0.09 lb/mmBtu. Mot. Amend 2 at 5, 12. The Agency also proposed to add an
emissions limitation of 0.142 lb/mmBtu for a recuperative reheat furnace combusting a
combination of natural gas and coke oven gas.
Id
.
In its first notice comments, the Agency proposed to amend the first two sentences
subsection (b) as follows:

74
[o]n and after January 1, 2012, no person shall cause or allow emissions of NO
x
into the atmosphere from any reverberatory furnace or crucible furnace use in
aluminum melting to exceed the following limitations. Compliance must be
demonstrated with the applicable emissions limitations on an ozone season and
annual basis. PC 17 at 5.
The Agency also proposed clarifying the emissions limitations in subsection (b)(1) and (b)(2).
Id
., citing In the Matter of: Nitrogen Oxides Emissions from Various Source Categories:
Amendments to 35 Ill. Adm. Code Parts 211 and 217, R08-19, slip op. at 105 (May 7, 2009).
Subpart M: Electrical Generating Units
Section 217.340: Applicability.
The Agency proposed to add a section addressing
applicability to EGUs, which provides in its entirety that, “[n]otwithstanding Subpart V or W of
this Part, the provisions of Subpart C of this Part and this Subpart apply to all fossil fuel-fired
stationary boilers subject to the CAIR NO
x
Trading Programs under Subpart D or E of Part 225
located at sources subject to this Subpart pursuant to Section 217.150 of this Part.” Prop. at 51;
see
Statement at 37-38;
supra
at 44-46 (discussing Section 217.150);
see generally
TSD at 5-45
(Industrial Boilers and Electrical Generating Unit Boilers).
In a question filed for the first hearing on October 14, 2008, Midwest Generation
suggested that the “all fossil fuel-fired stationary boilers” language in Section 217.340 could be
construed to expand the scope of Section 217.150(a)(2), which refers to “any . . . fossil fuel-fired
stationary boiler . . . that emits NO
x
in an amount equal to or greater than 15 tons per year and
equal to or greater than five tons per ozone season.” MG Questions at 2;
see
Prop. at 26
(proposed Section 217.150(a)(2)). Midwest Generation questioned whether the Agency intended
“to expand the applicability of the rule in this way.” MG Questions at 2. The Agency responded
by expressing the intent “that each Subpart apply to all of the affected emission units at an
affected source,
e.g.
, ‘any’ emission unit that meets the applicability criteria.” MG Answers at 3.
In another question filed for the first hearing, Midwest Generation noted that “[t]he TSD
claims there are a total of 18 EGUs subject to the rule, while the Statement of Reasons says there
are 20 ‘fossil fuel-fired stationary boilers’ subject to the rule.” MG Questions at 4. Midwest
Generation asked whether there are “fossil fuel-fired stationary boilers that are not EGUs that are
subject to the rule?”
Id
. The Agency responded that “there are 20 EGU boilers,” clarifying that
“there are two instances in which one unit is comprised of two boilers.” MG Answers at 8, citing
TSD at Appendices – 27 (Table E-1).
In another question filed for the first hearing, Midwest Generation stated that, “[b]ased
upon the proposed applicability language in Subpart M, Section 217.340, [and] assuming the
D.C. Circuit Court issues the mandate implementing its decision in the appeal of the CAIR,
EGUs would be subject to the provisions of Subpart D.” MG Questions at 3. Midwest
Generation consequently asked whether the Agency would consider amending this provision as
follows:

75
[n]otwithstanding Subpart V or W of this Part, the provisions of Subpart C of
this Part and this Subpart apply to all fossil fuel-fired stationary boilers subject to
the CAIR NO
x
Trading Programs under Subpart D or E of Part 225 any fossil
fuel-fired stationary boiler serving a generator that has a nameplate capacity
greater than 25 MWe and produces electricity for sale, excluding any units listed
in Appendix D of this Part, located at sources subject to this Subpart pursuant to
Section 217.150 of this Part.
Id
.
Responding to Midwest Generation, the Agency stated that it was “amenable” to
amending its proposed definition in the following fashion:
[n]otwithstanding Subpart V or W of this Part, the provisions of Subpart C of this
Part and this Subpart apply to all fossil fuel-fired stationary boilers subject to the
CAIR NO
x
Trading Programs under Subpart D or E of Part 225 any fossil fuel-
fired stationary boiler serving at any time a generator that has a nameplate
capacity greater than 25 MWe and produces electricity for sale, excluding any
units listed in Appendix D of this Part, located at sources subject to this Subpart
pursuant to Section 217.150 of this Part. MG Answers at 4-5;
see
Exh. 12 at 2-3
(Encouraging adoption of amended language).
In its first motion to amend its rulemaking proposal, the Agency recommended that the
Board “[a]mend Section 217.340 to reflect the provisions as previously agreed to between the
Illinois EPA and Midwest Generation as reflected in the Illinois EPA’s Answers to Midwest
Generation’s Questions for Agency Witnesses, filed September 30, 2008, and the October 14,
2008, hearing.” Mot. Amend 1 at 9;
see
MG Question at 3, MG Answers at 4-5.
In its post-hearing comments, Midwest Generation stated that,
[w]ith the amendments proposed to the Board by the Agency in its Motion to
Amend Rulemaking Proposal ("Agency's Motion") filed January 30, 2009,
Midwest Generation generally supports the Agency's proposal as it applies to
electric generating units ("EGUs"). The proposed amendments incorporate by
reference provisions agreed to between the Agency and Midwest Generation as
part of the Agency's Answers to Midwest Generation's Questions for Agency
Witnesses ("Agency's Answers"), which were filed before this Board on
September 30, 2008. PC 9 at 1-2 (noting Agency’s proposed amendment of
Section 217.340);
see
Mot. Amend 1 at 9, Tr.1 at 199-200.
In testimony filed for the second hearing on December 9, 2008, Mr. Kolaz argued that
“the CAIR rule should be considered RACT for EGUs” and that “Subpart M is unnecessary for
purposes of achieving the Agency’s stated goals of achieving RACT level reductions.” Exh. 6 at
25;
see
Tr.2 at 80-81. Midwest Generation concurred that Subpart M “is not necessary and
should be deleted from the rule.” Tr.3 at 58 (Miller testimony).

76
In its first notice comments, the Agency proposed to amend Section 217.340 “by adding
reference to and ‘fossil’ fuel-fired stationary boilers serving ‘at any time’ a generator,” reading
as follows:
[n]otwithstanding Subpart V or W of the Part, the provisions of Subpart D of this
Part and this Subpart apply to any fossil fuel-fired stationary boiler serving at any
time a generator that has a nameplate capacity greater than 25MWe and produces
electricity for sale, excluding any units listed in Appendix D of this Part, located
at sources subject to this Subpart pursuant to Section 217.150. PC 17 at 5, citing
In the Matter of: Nitrogen Oxides Emissions from Various Source Categories:
Amendments to 35 Ill. Adm. Code Parts 211 and 217, R08-19, slip op. at 55-56
(May 7, 2009).
Section 217.342: Exemptions.
The Agency proposed to add a section addressing
exemptions. The proposed subsection (a) provided in its entirety that, “[n]otwithstanding
Section 217.340 of this Subpart, the provisions of this Subpart do not apply to a fossil fuel-fired
stationary boiler operating under a federally enforceable limit of NO
x
emissions from such boiler
to less than 15 tons per year and less than five tons per ozone season.” Prop. at 51;
see
Statement
at 38, Kaleel Pre-filed Test. at 3. Proposed subsection (b) provided in its entirety that,
“[n]owithstanding Section 217.340 of this Subpart, the provisions of this Subpart do not apply to
a coal-fired stationary boiler that commenced operation before January 1, 2008, that is
complying with the multi-pollutant standard under Section 225.233 of Part 225 or the combined
pollutant standards under Subpart F of Part 225.” Prop. at 51;
see
Statement at 38.
In a question filed for the first hearing on October 14, 2008, Midwest Generation stated
that, “[b]ased upon the proposed applicability language in Subpart M, Section 217.340, [and]
assuming the D.C. Circuit Court issues the mandate implementing its decision in the appeal of
the CAIR, EGUs would be subject to the provisions of Subpart D.” MG Questions at 3.
Midwest Generation consequently asked whether the Agency would consider amending
subsection (b) of this provision as follows: “[n]otwithstanding section 217.340 of this Subpart,
the provisions of this Subpart do not apply to a coal-fired stationary boiler that commenced
operation before January 1, 2008, that is complying with Part 225.Subpart B through
the multi-
pollutant standard under Section 225.233 of Part 225 or the combined pollutant standards under
Subpart F of Part 225.”
Id
. Responding to Midwest Generation, the Agency stated that it was
“amenable” to amending subsection (b) in that fashion. MG Answers at 4-6.
In its post-hearing comments, Midwest Generation states that,
[w]ith the amendments proposed to the Board by the Agency in its Motion to
Amend Rulemaking Proposal ("Agency's Motion") filed January 30, 2009,
Midwest Generation generally supports the Agency's proposal as it applies to
electric generating units ("EGUs"). The proposed amendments incorporate by
reference provisions agreed to between the Agency and Midwest Generation as
part of the Agency's Answers to Midwest Generation's Questions for Agency
Witnesses ("Agency's Answers"), which were filed before this Board on

77
September 30, 2008. PC 9 at 1-2 (noting Agency’s proposed amendment of
Section 217.340);
see
Mot. Amend 1 at 10, Tr.1 at 199-200.
In its first notice comments, the Agency proposed, in light of the Board’s recent
rulemaking addressing mercury monitoring, to amend subsection (b) to read as follows:
“[n]otwithstanding Section 217.340, the provisions of this Subpart do not apply to a coal-fired
stationary boiler that commenced operation before January 1, 2008, that is complying with Part
225.Subpart B through the multi-pollutant standard or the combined pollutant standard.” PC 17
at 5;
see
In the Matter of: Amendments to 35 Ill. Adm. Code 225: Control of Emissions from
Large Combustion Sources (Mercury Monitoring), R09-10.
Section 217.344: Emissions Limitations.
The Agency proposed to add a new section
addressing emission limitations for EGUs. Statement at 38-39; Prop. at 51-52. Originally, the
Agency proposed that, “[o]n and after May 1, 2010, no person shall cause or allow emissions of
NO
x
into the atmosphere from any fossil fuel-fired stationary boiler” to exceed specified
limitations. Prop. at 50;
see
Statement at 37. The Agency proposed specific emissions
limitations based on the unit’s type. Prop. at 52 (proposed subsections (a), (b), and (c)). The
Agency also proposed that “[c]ompliance must be demonstrated with the emissions limitations
on an ozone season and annual basis.” Prop. at 51;
see
Statement at 39.
In its first motion to amend its rulemaking proposal, the Agency proposed to amend the
first sentence of Section 217.344 by extending the compliance deadline to January 1, 2012. Mot.
Amend 1 at 10. The Agency also proposed to change the emissions limitation for a boiler
combusting solid fuel from 0.09 lb/mmBtu to 0.012 lb/mmBtu.
Id
.;
see
MG Answers at 6-8
(providing basis for determining 0.09 lb/mmBtu constitutes RACT)
Section 217.345: Combination of Fuels.
The Agency proposed to add a new section
addressing combination of fuels, which provides in its entirety that “[t]he owner or operator of a
fossil fuel-fired stationary boiler subject to this Subpart and operated with any combination of
fuels must comply with a heat input weighted average emissions limitation to demonstrate
compliance with Section 217.344 of this Subpart.” Prop. at 52;
see
Statement at 39.
Appendix H
In the second motion to amend its rulemaking proposal, the Agency proposes to add an
Appendix H “to set forth the compliance dates for certain emission units at petroleum refineries.”
Mot. Amend 2 at 5, 13-14.
In its first notice comments, the Agency proposed corrections to the tables comprising
Appendix H. PC 17 at 6;
see
PC 16 at 14 (suggesting corrections to Appendix H in IERG
comment).
ORDER

78
The Board directs the Clerk to file the following proposed amendments with the Joint
Committee on Administrative Rules for second-notice review. Proposed additions are
underlined, and proposed deletions appear stricken.
TITLE 35: ENVIRONMENTAL PROTECTION
SUBTITLE B: AIR POLLUTION
CHAPTER I: POLLUTION CONTROL BOARD
SUBCHAPTER c: EMISSION STANDARDS AND LIMITATIONS FOR
STATIONARY SOURCES
PART 211
DEFINITIONS AND GENERAL PROVISIONS
SUBPART A: GENERAL PROVISIONS
Section
211.101
Incorporations by Reference
211.102
Abbreviations and Conversion Factors
SUBPART B: DEFINITIONS
Section
211.121
Other Definitions
211.122
Definitions (Repealed)
211.130
Accelacota
211.150
Accumulator
211.170
Acid Gases
211.210
Actual Heat Input
211.230
Adhesive
211.240
Adhesion Promoter
211.250
Aeration
211.270
Aerosol Can Filling Line
211.290
Afterburner
211.310
Air Contaminant
211.330
Air Dried Coatings
211.350
Air Oxidation Process
211.370
Air Pollutant
211.390
Air Pollution
211.410
Air Pollution Control Equipment
211.430
Air Suspension Coater/Dryer
211.450
Airless Spray
211.470
Air Assisted Airless Spray
211.474
Alcohol
211.479
Allowance
211.484
Animal
211.485
Animal Pathological Waste
211.490
Annual Grain Through-Put

79
211.495
Anti-Glare/Safety Coating
211.510
Application Area
211.530
Architectural Coating
211.550
As Applied
211.560
As-Applied Fountain Solution
211.570
Asphalt
211.590
Asphalt Prime Coat
211.610
Automobile
211.630
Automobile or Light-Duty Truck Assembly Source or Automobile or Light-Duty
Truck Manufacturing Plant
211.650
Automobile or Light-Duty Truck Refinishing
211.660
Automotive/Transportation Plastic Parts
211.665
Auxiliary Boiler
211.670
Baked Coatings
211.680
Bakery Oven
211.685
Basecoat/Clearcoat System
211.690
Batch Loading
211.695
Batch Operation
211.696
Batch Process Train
211.710
Bead-Dipping
211.730
Binders
211.740
Brakehorsepower (rated-bhp)
211.750
British Thermal Unit
211.770
Brush or Wipe Coating
211.790
Bulk Gasoline Plant
211.810
Bulk Gasoline Terminal
211.820
Business Machine Plastic Parts
211.830
Can
211.850
Can Coating
211.870
Can Coating Line
211.890
Capture
211.910
Capture Device
211.930
Capture Efficiency
211.950
Capture System
211.953
Carbon Adsorber
211.955
Cement
211.960
Cement Kiln
211.970
Certified Investigation
211.980
Chemical Manufacturing Process Unit
211.990
Choke Loading
211.995
Circulating Fluidized Bed Combustor
211.1010
Clean Air Act
211.1050
Cleaning and Separating Operation
211.1070
Cleaning Materials
211.1090
Clear Coating
211.1110
Clear Topcoat

80
211.1120
Clinker
211.1130
Closed Purge System
211.1150
Closed Vent System
211.1170
Coal Refuse
211.1190
Coating
211.1210
Coating Applicator
211.1230
Coating Line
211.1250
Coating Plant
211.1270
Coil Coating
211.1290
Coil Coating Line
211.1310
Cold Cleaning
211.1312
Combined Cycle System
211.1315
Combustion Tuning
211.1316
Combustion Turbine
211.1320
Commence Commercial Operation
211.1324
Commence Operation
211.1328
Common Stack
211.1330
Complete Combustion
211.1350
Component
211.1370
Concrete Curing Compounds
211.1390
Concentrated Nitric Acid Manufacturing Process
211.1410
Condensate
211.1430
Condensible PM-10
211.1435
Container Glass
211.1465
Continuous Automatic Stoking
211.1467
Continuous Coater
211.1470
Continuous Process
211.1490
Control Device
211.1510
Control Device Efficiency
211.1515
Control Period
211.1520
Conventional Air Spray
211.1530
Conventional Soybean Crushing Source
211.1550
Conveyorized Degreasing
211.1570
Crude Oil
211.1590
Crude Oil Gathering
211.1610
Crushing
211.1630
Custody Transfer
211.1650
Cutback Asphalt
211.1670
Daily-Weighted Average VOM Content
211.1690
Day
211.1710
Degreaser
211.1730
Delivery Vessel
211.1740
Diesel Engine
211.1750
Dip Coating
211.1770
Distillate Fuel Oil
211.1780
Distillation Unit

81
211.1790
Drum
211.1810
Dry Cleaning Operation or Dry Cleaning Facility
211.1830
Dump-Pit Area
211.1850
Effective Grate Area
211.1870
Effluent Water Separator
211.1875
Elastomeric Materials
211.1880
Electromagnetic Interference/Radio Frequency Interference (EMI/RFI) Shielding
Coatings
211.1885
Electronic Component
211.1890
Electrostatic Bell or Disc Spray
211.1900
Electrostatic Prep Coat
211.1910
Electrostatic Spray
211.1920
Emergency or Standby Unit
211.1930
Emission Rate
211.1950
Emission Unit
211.1970
Enamel
211.1990
Enclose
211.2010
End Sealing Compound Coat
211.2030
Enhanced Under-the-Cup Fill
211.2050
Ethanol Blend Gasoline
211.2070
Excess Air
211.2080
Excess Emissions
211.2090
Excessive Release
211.2110
Existing Grain-Drying Operation (Repealed)
211.2130
Existing Grain-Handling Operation (Repealed)
211.2150
Exterior Base Coat
211.2170
Exterior End Coat
211.2190
External Floating Roof
211.2210
Extreme Performance Coating
211.2230
Fabric Coating
211.2250
Fabric Coating Line
211.2270
Federally Enforceable Limitations and Conditions
211.2285
Feed Mill
211.2290
Fermentation Time
211.2300
Fill
211.2310
Final Repair Coat
211.2330
Firebox
211.2350
Fixed-Roof Tank
211.2355
Flare
211.2357
Flat Glass
211.2360
Flexible Coating
211.2365
Flexible Operation Unit
211.2370
Flexographic Printing
211.2390
Flexographic Printing Line
211.2410
Floating Roof
211.2420
Fossil Fuel

82
211.2425
Fossil Fuel-Fired
211.2430
Fountain Solution
211.2450
Freeboard Height
211.2470
Fuel Combustion Emission Unit or Fuel Combustion Emission Source
211.2490
Fugitive Particulate Matter
211.2510
Full Operating Flowrate
211.2530
Gas Service
211.2550
Gas/Gas Method
211.2570
Gasoline
211.2590
Gasoline Dispensing Operation or Gasoline Dispensing Facility
211.2610
Gel Coat
211.2620
Generator
211.2625
Glass Melting Furnace
211.2630
Gloss Reducers
211.2650
Grain
211.2670
Grain-Drying Operation
211.2690
Grain-Handling and Conditioning Operation
211.2710
Grain-Handling Operation
211.2730
Green-Tire Spraying
211.2750
Green Tires
211.2770
Gross Heating Value
211.2790
Gross Vehicle Weight Rating
211.2810
Heated Airless Spray
211.2815
Heat Input
211.2820
Heat Input Rate
211.2830
Heatset
211.2850
Heatset Web Offset Lithographic Printing Line
211.2870
Heavy Liquid
211.2890
Heavy Metals
211.2910
Heavy Off-Highway Vehicle Products
211.2930
Heavy Off-Highway Vehicle Products Coating
211.2950
Heavy Off-Highway Vehicle Products Coating Line
211.2970
High Temperature Aluminum Coating
211.2990
High Volume Low Pressure (HVLP) Spray
211.3010
Hood
211.3030
Hot Well
211.3050
Housekeeping Practices
211.3070
Incinerator
211.3090
Indirect Heat Transfer
211.3100
Industrial Boiler
211.3110
Ink
211.3130
In-Process Tank
211.3150
In-Situ Sampling Systems
211.3170
Interior Body Spray Coat
211.3190
Internal-Floating Roof
211.3210
Internal Transferring Area

83
211.3230
Lacquers
211.3250
Large Appliance
211.3270
Large Appliance Coating
211.3290
Large Appliance Coating Line
211.3300
Lean-Burn Engine
211.3310
Light Liquid
211.3330
Light-Duty Truck
211.3350
Light Oil
211.3355
Lime Kiln
211.3370
Liquid/Gas Method
211.3390
Liquid-Mounted Seal
211.3410
Liquid Service
211.3430
Liquids Dripping
211.3450
Lithographic Printing Line
211.3470
Load-Out Area
211.3475
Load Shaving Unit
211.3480
Loading Event
211.3483
Long Dry Kiln
211.3485
Long Wet Kiln
211.3487
Low-NOx Burner
211.3490
Low Solvent Coating
211.3500
Lubricating Oil
211.3510
Magnet Wire
211.3530
Magnet Wire Coating
211.3550
Magnet Wire Coating Line
211.3570
Major Dump Pit
211.3590
Major Metropolitan Area (MMA)
211.3610
Major Population Area (MPA)
211.3620
Manually Operated Equipment
211.3630
Manufacturing Process
211.3650
Marine Terminal
211.3660
Marine Vessel
211.3670
Material Recovery Section
211.3690
Maximum Theoretical Emissions
211.3695
Maximum True Vapor Pressure
211.3710
Metal Furniture
211.3730
Metal Furniture Coating
211.3750
Metal Furniture Coating Line
211.3770
Metallic Shoe-Type Seal
211.3780
Mid-Kiln Firing
211.3790
Miscellaneous Fabricated Product Manufacturing Process
211.3810
Miscellaneous Formulation Manufacturing Process
211.3830
Miscellaneous Metal Parts and Products
211.3850
Miscellaneous Metal Parts and Products Coating
211.3870
Miscellaneous Metal Parts or Products Coating Line
211.3890
Miscellaneous Organic Chemical Manufacturing Process

84
211.3910
Mixing Operation
211.3915
Mobile Equipment
211.3930
Monitor
211.3950
Monomer
211.3960
Motor Vehicles
211.3965
Motor Vehicle Refinishing
211.3970
Multiple Package Coating
211.3980
Nameplate Capacity
211.3990
New Grain-Drying Operation (Repealed)
211.4010
New Grain-Handling Operation (Repealed)
211.4030
No Detectable Volatile Organic Material Emissions
211.4050
Non-Contact Process Water Cooling Tower
211.4055
Non-Flexible Coating
211.4065
Non-Heatset
211.4067
NOx Trading Program
211.4070
Offset
211.4090
One Hundred Percent Acid
211.4110
One-Turn Storage Space
211.4130
Opacity
211.4150
Opaque Stains
211.4170
Open Top Vapor Degreasing
211.4190
Open-Ended Valve
211.4210
Operator of a Gasoline Dispensing Operation or Operator of a Gasoline
Dispensing Facility
211.4230
Organic Compound
211.4250
Organic Material and Organic Materials
211.4260
Organic Solvent
211.4270
Organic Vapor
211.4280
Other Glass
211.4290
Oven
211.4310
Overall Control
211.4330
Overvarnish
211.4350
Owner of a Gasoline Dispensing Operation or Owner of a Gasoline Dispensing
Facility
211.4370
Owner or Operator
211.4390
Packaging Rotogravure Printing
211.4410
Packaging Rotogravure Printing Line
211.4430
Pail
211.4450
Paint Manufacturing Source or Paint Manufacturing Plant
211.4470
Paper Coating
211.4490
Paper Coating Line
211.4510
Particulate Matter
211.4530
Parts Per Million (Volume) or PPM (Vol)
211.4550
Person
211.4590
Petroleum
211.4610
Petroleum Liquid

85
211.4630
Petroleum Refinery
211.4650
Pharmaceutical
211.4670
Pharmaceutical Coating Operation
211.4690
Photochemically Reactive Material
211.4710
Pigmented Coatings
211.4730
Plant
211.4740
Plastic Part
211.4750
Plasticizers
211.4770
PM-10
211.4790
Pneumatic Rubber Tire Manufacture
211.4810
Polybasic Organic Acid Partial Oxidation Manufacturing Process
211.4830
Polyester Resin Material(s)
211.4850
Polyester Resin Products Manufacturing Process
211.4870
Polystyrene Plant
211.4890
Polystyrene Resin
211.4910
Portable Grain-Handling Equipment
211.4930
Portland Cement Manufacturing Process Emission Source
211.4950
Portland Cement Process or Portland Cement Manufacturing Plant
211.4960
Potential Electrical Output Capacity
211.4970
Potential to Emit
211.4990
Power Driven Fastener Coating
211.5010
Precoat
211.5015
Preheater Kiln
211.5020
Preheater/Precalciner Kiln
211.5030
Pressure Release
211.5050
Pressure Tank
211.5060
Pressure/Vacuum Relief Valve
211.5061
Pretreatment Wash Primer
211.5065
Primary Product
211.5070
Prime Coat
211.5080
Primer Sealer
211.5090
Primer Surfacer Coat
211.5110
Primer Surfacer Operation
211.5130
Primers
211.5150
Printing
211.5170
Printing Line
211.5185
Process Emission Source
211.5190
Process Emission Unit
211.5195
Process Heater
211.5210
Process Unit
211.5230
Process Unit Shutdown
211.5245
Process Vent
211.5250
Process Weight Rate
211.5270
Production Equipment Exhaust System
211.5310
Publication Rotogravure Printing Line
211.5330
Purged Process Fluid

86
211.5340
Rated Heat Input Capacity
211.5350
Reactor
211.5370
Reasonably Available Control Technology (RACT)
211.5390
Reclamation System
211.5410
Refiner
211.5430
Refinery Fuel Gas
211.5450
Refinery Fuel Gas System
211.5470
Refinery Unit or Refinery Process Unit
211.5480
Reflective Argent Coating
211.5490
Refrigerated Condenser
211.5500
Regulated Air Pollutant
211.5510
Reid Vapor Pressure
211.5530
Repair
211.5550
Repair Coat
211.5570
Repaired
211.5580
Repowering
211.5590
Residual Fuel Oil
211.5600
Resist Coat
211.5610
Restricted Area
211.5630
Retail Outlet
211.5640
Rich-Burn Engine
211.5650
Ringelmann Chart
211.5670
Roadway
211.5690
Roll Coater
211.5710
Roll Coating
211.5730
Roll Printer
211.5750
Roll Printing
211.5770
Rotogravure Printing
211.5790
Rotogravure Printing Line
211.5810
Safety Relief Valve
211.5830
Sandblasting
211.5850
Sanding Sealers
211.5870
Screening
211.5880
Screen Printing on Paper
211.5890
Sealer
211.5910
Semi-Transparent Stains
211.5930
Sensor
211.5950
Set of Safety Relief Valves
211.5970
Sheet Basecoat
211.5980
Sheet-Fed
211.5990
Shotblasting
211.6010
Side-Seam Spray Coat
211.6025
Single Unit Operation
211.6030
Smoke
211.6050
Smokeless Flare
211.6060
Soft Coat

87
211.6070
Solvent
211.6090
Solvent Cleaning
211.6110
Solvent Recovery System
211.6130
Source
211.6140
Specialty Coatings
211.6145
Specialty Coatings for Motor Vehicles
211.6150
Specialty High Gloss Catalyzed Coating
211.6170
Specialty Leather
211.6190
Specialty Soybean Crushing Source
211.6210
Splash Loading
211.6230
Stack
211.6250
Stain Coating
211.6270
Standard Conditions
211.6290
Standard Cubic Foot (scf)
211.6310
Start-Up
211.6330
Stationary Emission Source
211.6350
Stationary Emission Unit
211.6355
Stationary Gas Turbine
211.6360
Stationary Reciprocating Internal Combustion Engine
211.6370
Stationary Source
211.6390
Stationary Storage Tank
211.6400
Stencil Coat
211.6410
Storage Tank or Storage Vessel
211.6420
Strippable Spray Booth Coating
211.6430
Styrene Devolatilizer Unit
211.6450
Styrene Recovery Unit
211.6470
Submerged Loading Pipe
211.6490
Substrate
211.6510
Sulfuric Acid Mist
211.6530
Surface Condenser
211.6540
Surface Preparation Materials
211.6550
Synthetic Organic Chemical or Polymer Manufacturing Plant
211.6570
Tablet Coating Operation
211.6580
Texture Coat
211.6590
Thirty-Day Rolling Average
211.6610
Three-Piece Can
211.6620
Three or Four Stage Coating System
211.6630
Through-the-Valve Fill
211.6650
Tooling Resin
211.6670
Topcoat
211.6690
Topcoat Operation
211.6695
Topcoat System
211.6710
Touch-Up
211.6720
Touch-Up Coating
211.6730
Transfer Efficiency
211.6750
Tread End Cementing

88
211.6770
True Vapor Pressure
211.6790
Turnaround
211.6810
Two-Piece Can
211.6830
Under-the-Cup Fill
211.6850
Undertread Cementing
211.6860
Uniform Finish Blender
211.6870
Unregulated Safety Relief Valve
211.6880
Vacuum Metallizing
211.6890
Vacuum Producing System
211.6910
Vacuum Service
211.6930
Valves Not Externally Regulated
211.6950
Vapor Balance System
211.6970
Vapor Collection System
211.6990
Vapor Control System
211.7010
Vapor-Mounted Primary Seal
211.7030
Vapor Recovery System
211.7050
Vapor-Suppressed Polyester Resin
211.7070
Vinyl Coating
211.7090
Vinyl Coating Line
211.7110
Volatile Organic Liquid (VOL)
211.7130
Volatile Organic Material Content (VOMC)
211.7150
Volatile Organic Material (VOM) or Volatile Organic Compound (VOC)
211.7170
Volatile Petroleum Liquid
211.7190
Wash Coat
211.7200
Washoff Operations
211.7210
Wastewater (Oil/Water) Separator
211.7230
Weak Nitric Acid Manufacturing Process
211.7250
Web
211.7270
Wholesale Purchase - Consumer
211.7290
Wood Furniture
211.7310
Wood Furniture Coating
211.7330
Wood Furniture Coating Line
211.7350
Woodworking
211.7400
Yeast Percentage
211.APPENDIX A
Rule into Section Table
211.APPENDIX B
Section into Rule Table
AUTHORITY: Implementing Sections 9, 9.1, 9.9 and 10 and authorized by Sections 27 and 28
of the Environmental Protection Act [415 ILCS 5/9, 9.1, 9.9, 10, 27 and 28].
SOURCE: Adopted as Chapter 2: Air Pollution, Rule 201: Definitions, R71-23, 4 PCB 191,
filed and effective April 14, 1972; amended in R74-2 and R75-5, 32 PCB 295, at 3 Ill. Reg. 5, p.
777, effective February 3, 1979; amended in R78-3 and 4, 35 PCB 75 and 243, at 3 Ill. Reg. 30,
p. 124, effective July 28, 1979; amended in R80-5, at 7 Ill. Reg. 1244, effective January 21,
1983; codified at 7 Ill. Reg. 13590; amended in R82-1 (Docket A) at 10 Ill. Reg. 12624, effective

89
July 7, 1986; amended in R85-21(A) at 11 Ill. Reg. 11747, effective June 29, 1987; amended in
R86-34 at 11 Ill. Reg. 12267, effective July 10, 1987; amended in R86-39 at 11 Ill. Reg. 20804,
effective December 14, 1987; amended in R82-14 and R86-37 at 12 Ill. Reg. 787, effective
December 24, 1987; amended in R86-18 at 12 Ill. Reg. 7284, effective April 8, 1988; amended
in R86-10 at 12 Ill. Reg. 7621, effective April 11, 1988; amended in R88-23 at 13 Ill. Reg.
10862, effective June 27, 1989; amended in R89-8 at 13 Ill. Reg. 17457, effective January 1,
1990; amended in R89-16(A) at 14 Ill. Reg. 9141, effective May 23, 1990; amended in R88-
30(B) at 15 Ill. Reg. 5223, effective March 28, 1991; amended in R88-14 at 15 Ill. Reg. 7901,
effective May 14, 1991; amended in R91-10 at 15 Ill. Reg. 15564, effective October 11, 1991;
amended in R91-6 at 15 Ill. Reg. 15673, effective October 14, 1991; amended in R91-22 at 16
Ill. Reg. 7656, effective May 1, 1992; amended in R91-24 at 16 Ill. Reg. 13526, effective August
24, 1992; amended in R93-9 at 17 Ill. Reg. 16504, effective September 27, 1993; amended in
R93-11 at 17 Ill. Reg. 21471, effective December 7, 1993; amended in R93-14 at 18 Ill. Reg.
1253, effective January 18, 1994; amended in R94-12 at 18 Ill. Reg. 14962, effective September
21, 1994; amended in R94-14 at 18 Ill. Reg. 15744, effective October 17, 1994; amended in
R94-15 at 18 Ill. Reg. 16379, effective October 25, 1994; amended in R94-16 at 18 Ill. Reg.
16929, effective November 15, 1994; amended in R94-21, R94-31 and R94-32 at 19 Ill. Reg.
6823, effective May 9, 1995; amended in R94-33 at 19 Ill. Reg. 7344, effective May 22, 1995;
amended in R95-2 at 19 Ill. Reg. 11066, effective July 12, 1995; amended in R95-16 at 19 Ill.
Reg. 15176, effective October 19, 1995; amended in R96-5 at 20 Ill. Reg. 7590, effective May
22, 1996; amended in R96-16 at 21 Ill. Reg. 2641, effective February 7, 1997; amended in R97-
17 at 21 Ill. Reg. 6489, effective May 16, 1997; amended in R97-24 at 21 Ill. Reg. 7695,
effective June 9, 1997; amended in R96-17 at 21 Ill. Reg. 7856, effective June 17, 1997;
amended in R97-31 at 22 Ill. Reg. 3497, effective February 2, 1998; amended in R98-17 at 22 Ill.
Reg. 11405, effective June 22, 1998; amended in R01-9 at 25 Ill. Reg. 108, effective December
26, 2000; amended in R01-11 at 25 Ill. Reg. 4597, effective March 15, 2001; amended in R01-17
at 25 Ill. Reg. 5900, effective April 17, 2001; amended in R05-16 at 29 Ill. Reg. 8181, effective
May 23, 2005; amended in R05-11 at 29 Ill. Reg.8892, effective June 13, 2005; amended in R04-
12/20 at 30 Ill. Reg. 9654, effective May 15, 2006; amended in R07-18 at 31 Ill. Reg. 14254,
effective September 25, 2007; amended in R08-6 at 32 Ill. Reg. 1387, effective January 16,
2008; amended in R08-19 at 33 Ill. Reg. ____, effective __________.
SUBPART B: DEFINITIONS
Section 211.665 Auxiliary Boiler
“Auxiliary boiler” means, for purposes of Part 217, a boiler that is operated only when the main
boiler or boilers at a source are not in service and is used either to maintain building heat or to
assist in the startup of the main boiler or boilers. This term does not include emergency or
standby units and load shaving units.
(Source: Added at 33 Ill. Reg. _____, effective __________)
Section 211.995 Circulating Fluidized Bed Combustor

90
“Circulating fluidized bed combustor” means, for purposes of Part 217, a fluidized bed
combustor in which the majority of the fluidized bed material is carried out of the primary
combustion zone and is transported back to the primary zone through a recirculation loop.
(Source: Added at 33 Ill. Reg. _____, effective ___________)
Section 211.1315 Combustion Tuning
“Combustion tuning” means, for purposes of Part 217, review and adjustment of a combustion
process to maintain combustion efficiency of an emission unit, as performed in accordance with
procedures provided by the manufacturer or by a trained technician.
(Source: Added at 33 Ill. Reg. _____, effective ______________)
Section 211.1435 Container Glass
“Container glass” means, for purposes of Part 217, glass made of soda-lime recipe, clear or
colored, which is pressed or blown, or both, into bottles, jars, ampoules, and other products listed
in Standard Industrial Classification 3221.
(Source: Added at 33 Ill. Reg. _____, effective ___________)
Section 211.2355 Flare
“Flare” means an open combustor without enclosure or shroud.
(Source: Added at 33 Ill. Reg. _____, effective ___________)
Section 211.2357 Flat Glass
“Flat glass” means, for purposes of Part 217, glass made of soda-lime recipe and produced into
continuous flat sheets and other products listed in Standard Industrial Classification 3211.
(Source: Added at 33 Ill. Reg. _____, effective ___________)
Section 211.2625 Glass Melting Furnace
“Glass melting furnace” means, for purposes of Part 217, a unit comprising a refractory vessel in
which raw materials are charged and melted at high temperature to produce molten glass.
(Source: Added at 33 Ill. Reg. _____, effective ____________)
Section 211.3100 Industrial Boiler
“Industrial boiler” means, for purposes of Part 217, an enclosed vessel in which water is heated
and circulated either as hot water or as steam for heating or for power, or both. This term does

 
91
not include a heat recovery steam generator that captures waste heat from a combustion turbine
and boilers serving a generator that has a nameplate capacity greater than 25 MWe and produces
electricity for sale, and cogeneration units, if such boilers meet the applicability criteria under
Subpart M of Part 217.
(Source: Added at 33 Ill. Reg. _____, effective ___________)
Section 211.3355 Lime Kiln
“Lime kiln” means, for purposes of Part 217, an enclosed combustion device used to calcine lime
mud, which consists primarily of calcium carbonate, into calcium oxide.
(Source: Added at 33 Ill. Reg. _____, effective ___________)
Section 211.3475 Load Shaving Unit
“Load shaving unit” means, for purposes of Part 217, a device used to generate electricity for
sale or use during high electric demand days, including but not limited to stationary reciprocating
internal combustion engines or turbines.
(Source: Added at 33 Ill. Reg. _____, effective ____________)
Section 211.4280 Other Glass
“Other glass” means, for purposes of Part 217, glass that is neither container glass, as that term is
defined in Section 211.1435, nor flat glass, as that term is defined in Section 211.2357.
(Source: Added at 33 Ill. Reg. _____, effective ____________)
Section 211.5195 Process Heater
“Process heater” means, for purposes of Part 217, an enclosed combustion device that burns
gaseous or liquid fuels only and that indirectly transfers heat to a process fluid or a heat transfer
medium other than water. This term does not include pipeline heaters and storage tank heaters
that are primarily meant to maintain fluids at a certain temperature or viscosity.
(Source: Added at 33 Ill. Reg. _____, effective ______________)
TITLE 35: ENVIRONMENTAL PROTECTION
SUBTITLE B: AIR POLLUTION
CHAPTER I: POLLUTION CONTROL BOARD
SUBCHAPTER c: EMISSION STANDARDS AND LIMITATIONS FOR STATIONARY
SOURCES

92
PART 217
NITROGEN OXIDES EMISSIONS
SUBPART A: GENERAL PROVISIONS
Section
217.100
Scope and Organization
217.101
Measurement Methods
217.102
Abbreviations and Units
217.103
Definitions
217.104
Incorporations by Reference
SUBPART B: NEW FUEL COMBUSTION EMISSION SOURCES
Section
217.121
New Emission Sources (Repealed)
SUBPART C: EXISTING FUEL COMBUSTION EMISSION UNITS SOURCES
Section
217.141
Existing Emission Units Sources in Major Metropolitan Areas
Section
217.150
Applicability
SUBPART D: NO
x
GENERAL REQUIREMENTS
217.152
Compliance Date
217.154
Performance Testing
217.155
Initial Compliance Certification
217.156
Recordkeeping and Reporting
217.157
Testing and Monitoring
217.158
Emissions Averaging Plans
SUBPART E: INDUSTRIAL BOILERS
Section
217.160
Applicability
217.162
Exemptions
217.164
Emissions Limitations
217.165
Combination of Fuels
217.166
Methods and Procedures for Combustion Tuning
SUBPART F: PROCESS HEATERS
Section
217.180
Applicability
217.182
Exemptions
217.184
Emissions Limitations
217.185
Combination of Fuels

93
217.186
Methods and Procedures for Combustion Tuning
SUBPART G: GLASS MELTING FURNANCES
Section
217.200
Applicability
217.202
Exemptions
217.204
Emissions Limitations
SUBPART H: CEMENT AND LIME KILNS
Section
217.220
Applicability
217.222
Exemptions
217.224
Emissions Limitations
SUBPART I: IRON AND STEEL AND ALUMINUM MANUFACTURING
Section
217.240
Applicability
217.242
Exemptions
217.244
Emissions Limitations
SUBPART K: PROCESS EMISSION SOURCES
Section
217.301
Industrial Processes
SUBPART M: ELECTRICAL GENERATING UNITS
Section
217.340
Applicability
217.342
Exemptions
217.344
Emissions Limitations
217.345
Combination of Fuels
SUBPART O: CHEMICAL MANUFACTURE
Section
217.381
Nitric Acid Manufacturing Processes
SUBPART Q: STATIONARY RECIPROCATING INTERNAL COMBUSTION
ENGINES AND TURBINES
Section
217.386
Applicability
217.388
Control and Maintenance Requirements
217.390
Emissions Averaging Plans

94
217.392
Compliance
217.394
Testing and Monitoring
217.396
Recordkeeping and Reporting
SUBPART T: CEMENT KILNS
Section
217.400
Applicability
217.402
Control Requirements
217.404
Testing
217.406
Monitoring
217.408
Reporting
217.410
Recordkeeping
SUBPART U: NOx CONTROL AND TRADING PROGRAM FOR
SPECIFIED NOx GENERATING UNITS
Section
217.450
Purpose
217.452
Severability
217.454
Applicability
217.456
Compliance Requirements
217.458
Permitting Requirements
217.460
Subpart U NOx Trading Budget
217.462
Methodology for Obtaining NOx Allocations
217.464
Methodology for Determining NOx Allowances from the New Source Set-Aside
217.466
NOx Allocations Procedure for Subpart U Budget Units
217.468
New Source Set-Asides for “New” Budget Units
217.470
Early Reduction Credits (ERCs) for Budget Units
217.472
Low-Emitter Requirements
217.474
Opt-In Units
217.476
Opt-In Process
217.478
Opt-In Budget Units: Withdrawal from NOx Trading Program
217.480
Opt-In Units: Change in Regulatory Status
217.482
Allowance Allocations to Opt-In Budget Units
SUBPART V: ELECTRIC POWER GENERATION
Section
217.521
Lake of Egypt Power Plant
217.700
Purpose
217.702
Severability
217.704
Applicability
217.706
Emission Limitations
217.708
NOx Averaging
217.710
Monitoring
217.712
Reporting and Recordkeeping

95
SUBPART W: NOx TRADING PROGRAM FOR ELECTRICAL
GENERATING UNITS
Section
217.750
Purpose
217.752
Severability
217.754
Applicability
217.756
Compliance Requirements
217.758
Permitting Requirements
217.760
NOx Trading Budget
217.762
Methodology for Calculating NOx Allocations for Budget Electrical
Generating Units (EGUs)
217.764
NOx Allocations for Budget EGUs
217.768
New Source Set-Asides for “New” Budget EGUs
217.770
Early Reduction Credits for Budget EGUs
217.774
Opt-In Units
217.776
Opt-In Process
217.778
Budget Opt-In Units: Withdrawal from NOx Trading Program
217.780
Opt-In Units: Change in Regulatory Status
217.782
Allowance Allocations to Budget Opt-In Units
SUBPART X: VOLUNTARY NOx EMISSIONS REDUCTION PROGRAM
Section
217.800
Purpose
217.805
Emission Unit Eligibility
217.810
Participation Requirements
217.815
NOx Emission Reductions and the Subpart X NOx Trading Budget
217.820
Baseline Emissions Determination
217.825
Calculation of Creditable NOx Emission Reductions
217.830
Limitations on NOx Emission Reductions
217.835
NOx Emission Reduction Proposal
217.840
Agency Action
217.845
Emissions Determination Methods
217.850
Emissions Monitoring
217.855
Reporting
217.860
Recordkeeping
217.865
Enforcement
217.APPENDIX A
Rule into Section Table
217.APPENDIX B
Section into Rule Table
217.APPENDIX C
Compliance Dates
217.APPENDIX D
Non-Electrical Generating Units
217.APPENDIX E
Large Non-Electrical Generating Units
217.APPENDIX F
Allowances for Electrical Generating Units
217.APPENDIX G
Existing Reciprocating Internal Combustion Engines Affected by the NO
x

 
96
SIP Call
217.APPENDIX H
Compliance Dates for Certain Emissions Units at Petroleum Refineries
AUTHORITY: Implementing Sections 9.9 and 10 and authorized by Sections 27 and 28 of the
Environmental Protection Act [415 ILCS 5/9.9, 10, 27 and 28].
SOURCE: Adopted as Chapter 2: Air Pollution, Rule 207: Nitrogen Oxides Emissions, R71-23,
4 PCB 191, April 13, 1972, filed and effective April 14, 1972; amended at 2 Ill. Reg. 17, p. 101,
effective April 13, 1978; codified at 7 Ill. Reg. 13609; amended in R01-9 at 25 Ill. Reg. 128,
effective December 26, 2000; amended in R01-11 at 25 Ill. Reg. 4597, effective March 15, 2001;
amended in R01-16 and R01-17 at 25 Ill. Reg. 5914, effective April 17, 2001; amended in R07-
18 at 31 Ill. Reg. 14271, effective September 25, 2007; amended in R08-19 at 33 Ill. Reg. ____,
effective _________.
SUBPART A: GENERAL PROVISIONS
Section 217.100 Scope and Organization
a)
This Part sets standards and limitations for emission of oxides of nitrogen from
stationary sources.
b)
Permits for sources subject to this Part may be required pursuant to 35 Ill. Adm.
Code 201 or Section 39.5 of the Act.
c)
Notwithstanding the provisions of this Part the air quality standards contained in
35 Ill. Adm. Code 243 may not be violated.
d)
These rules have been grouped for convenience of the public; the scope of each is
determined by its language and history.
(Source: Amended at 33 Ill. Reg. ___, effective ___________)
Section 217.104 Incorporations by Reference
The following materials are incorporated by reference. These incorporations do not include any
later amendments or editions.
a)
The phenol disulfonic acid procedures, as published in 40 CFR 60, Appendix A,
Method 7 (2000);
b)
40 CFR 96, subparts B, D, G, and H (1999);
c)
40 CFR 96.1 through 96.3, 96.5 through 96.7, 96.50 through 96.54, 96.55 (a) &
(b), 96.56 and 96.57 (1999);
d)
40 CFR 60, 72, 75 & 76 (2006);

97
e)
Alternative Control Techniques Document -- NO
x
Emissions from Cement
Manufacturing, EPA-453/R-94-004, U. S. Environmental Protection Agency-
Office of Air Quality Planning and Standards, Research Triangle Park, N. C.
27711, March 1994;
f)
Section 11.6, Portland Cement Manufacturing, AP-42 Compilation of Air
Emission Factors, Volume 1: Stationary Point and Area Sources, U.S.
Environmental Protection Agency-Office of Air Quality Planning and Standards,
Research Triangle Park, N. C. 27711, revised January 1995;
g)
40 CFR 60.13 (2001);
h)
40 CFR 60, Appendix A, Methods 3A, 7, 7A, 7C, 7D, 7E, 19, and 20 (2000);
i)
ASTM D6522-00, Standard Test Method for Determination of Nitrogen Oxides,
Carbon Monoxide, and Oxygen Concentrations in Emissions from Natural Gas-
Fired Reciprocating Engines, Combustion Turbines, Boilers, and Process Heaters
Using Portable Analyzers (2000);
jk)
Standards of Performance for Stationary Combustion Turbines, 40 CFR 60,
Subpart KKKK, 60.4400 (2006); and
kl)
Compilation of Air Pollutant Emission Factors: AP-42, Volume I: Stationary
Point and Area Sources (2000), USEPA;.
l)
40 CFR 60, Appendix A, Methods 1, 2, 3, and 4 (20072008
);
m)
Alternative Control Techniques Document - NO
x
Emissions from
Industrial/Commercial/Institutional (ICI) Boilers, EPA-453/R-94-022, U. S.
Environmental Protection Agency, Office of Air and Radiation, Office of Air
Quality Planning and Standards, Research Triangle Park, N. C. 27711, March
1994;
n)
Alternative Control Techniques Document - NO
x
Emissions from Process Heaters
(Revised), EPA-453/R-93-034, U. S. Environmental Protection Agency, Office of
Air and Radiation, Office of Air Quality Planning and Standards, Research
Triangle Park, N. C. 27711, September 1993;
o)
Alternative Control Techniques Document - NO
x
Emissions from Glass
Manufacturing, EPA-453/R-94-037, U. S. Environmental Protection Agency,
Office of Air and Radiation, Office of Air Quality Planning and Standards,
Research Triangle Park, N. C. 27711, June 1994; and
p)
Alternative Control Techniques Document - NO
x
Emissions from Iron and Steel
Mills, EPA-453/R-94-065, U. S. Environmental Protection Agency, Office of Air

 
98
and Radiation, Office of Air Quality Planning and Standards, Research Triangle
Park, N. C. 27711, September 1994;.
q)
40 CFR 60 and 75 (2008); and
r)
40 CFR 60, Appendix B, Performance Specification 16, 74 FR 12575 (March 25,
2009).
(Source: Amended at 33 Ill. Reg. _____, effective ___________)
SUBPART B: NEW FUEL COMBUSTION EMISSION SOURCES
Section 217.121 New Emission Sources (Repealed)
No person shall cause or allow the emission of nitrogen oxides (NO
X
) into the atmosphere in any
one hour period from any new fuel combustion emission source with an actual heat input equal
to or greater than 73.2 MW (250 mmbtu/hr) to exceed the following standards and limitations:
a)
For gaseous fossil fuel firing, 0.310 kg/MW-hr (0.20 lbs/mmbtu) of actual heat
input;
b)
For liquid fossil fuel firing, 0.464 kg/MW-hr (0.30 lbs/mmbtu) of actual heat
input;
c)
For dual gaseous and liquid fossil fuel firing, 0.464 kg/MW-hr (0.30 lbs/mmbtu)
of actual heat input;
d)
For solid fossil fuel firing, 1.08 kg/MW-hr (0.7 lbs./mmbtu) of actual heat input;
e)
For fuel combustion emission sources burning simultaneously any combination of
solid, liquid and gaseous fossil fuels, an allowable emission rate shall be
determined by the following equation:
E = (AG + BL + CS) Q
Where:
E = Allowable nitrogen oxides emissions rate
Q = Actual heat input derived from all fossil fuels
G = Percent of actual heat input derived from gaseous fossil fuel
L = Percent of actual heat input derived from liquid fossil fuel
S = Percent of actual heat input derived from solid fossil fuel
G + L + S = 100.0
and, where A, B, C and appropriate metric and English units are determined from
the following table:

 
99
Metric
English
E
kg/hr
lbs/hr
Q
MW
mmbtu/hr
A
0.023
0.003
B
0.023
0.003
C
0.053
0.007
(Source: Repealed at 33 Ill. Reg. _____, effective ___________)
SUBPART C: EXISTING FUEL COMBUSTION EMISSION UNITS SOURCES
Section 217.141 Existing Emission Units Sources in Major Metropolitan Areas
No person shall cause or allow the emission of nitrogen oxides into the atmosphere in any one
hour period from any existing fuel combustion emission unit source with an actual heat input
equal to or greater than 73.2 MW (250 mmbtu/hr), located in the Chicago or St. Louis (Illinois)
major metropolitan areas to exceed the following limitations:
a)
For gaseous and/or liquid fossil fuel firing, 0.46 kg/MW-hr (0.3 lbs/mmbtu) of
actual heat input;
b)
For solid fossil fuel firing, 1.39 kg/MW-hr (0.9 lbs/mmbtu) of actual heat input;
c)
For fuel combustion emission units sources burning simultaneously any
combination of solid, liquid and gaseous fuel, the allowable emission rate shall be
determined by the following equation:
E = (AG + BL + CS) Q
Where:
E
= allowable nitrogen oxides emissions rate
Q
= actual heat input
G
= percent of actual heat input derived from gaseous fossil fuel
L
= percent of actual heat input derived from liquid fossil fuel
S
= percent of actual heat input derived from solid fossil fuel
G + L + S
= 100.0
and where A, B, and C and appropriate metric and English units are determined from the
following table:
Metric
English
E
kg/hr
lbs/hr
Q
MW
mmbtu/hr
A
0.023
0.003

100
B
0.023
0.003
C
0.068
0.009
d)
Exceptions: This Section rule shall not apply to the following:
1)
Existing existing fuel combustion units sources that which are either
cyclone fired boilers burning solid or liquid fuel, or horizontally opposed
fired boilers burning solid fuel; or.
2)
Emission units that are subject to the emissions limitations of Subpart E,
F, G, H, M, or Q of this Part.
(Source: Amended at 33 Ill. Reg. _____, effective ______________)
SUBPART D: NO
x
GENERAL REQUIREMENTSINDUSTRIAL BOILERS
Section 217.150 Applicability
a)
Applicability
1)
The provisions of this Subpart and Subparts E, F, G, H, I and M of this
Part apply to the following:
A)
All sources that are located in either one of the following areas and
that emit or have the potential to emit NO
x
in an amount equal to
or greater than 100 tons per year:
i)
The area composed of the Chicago area counties of Cook,
DuPage, Kane, Lake, McHenry, and Will, the Townships
of Aux Sable and Goose Lake in Grundy County, and the
Township of Oswego in Kendall County; or
ii)
The area composed of the Metro East area counties of
Jersey, Madison, Monroe, and St. Clair, and the Township
of Baldwin in Randolph County; and
B)
Any industrial boiler, process heater, glass melting furnace, cement
kiln, lime kiln, iron and steel reheat, annealing, or galvanizing
furnace, aluminum reverberatory or crucible furnace, or fossil fuel-
fired stationary boiler at such sources described in subsection
(a)(1)(A) of this Section that emits NO
x
in an amount equal to or
greater than 15 tons per year and equal to or greater than five tons
per ozone season.
2)
For purposes of this Section, “potential to emit” means the quantity of
NO
x
that potentially could be emitted by a stationary source before add-on
controls based on the design capacity or maximum production capacity of

101
the source and 8,760 hours per year or the quantity of NO
x
that potentially
could be emitted by a stationary source as established in a federally
enforceable permit.
b)
If a source ceases to fulfill the emissions criteria of subsection (a) of this Section,
the requirements of this Subpart and Subpart E, F, G, H, I or M of this Part
continue to apply to any emission unit that was ever subject to the provisions of
any of those Subparts.
c)
The provisions of this Subpart do not apply to afterburners, flares, and
incinerators.
d)
Where a construction permit, for which the application was submitted to the
Agency prior to the adoption of this Subpart, is issued that relies on decreases in
emissions of NO
x
from existing emission units for purposes of netting or emission
offsets, such NO
x
decreases remain creditable notwithstanding any requirements
that may apply to the existing emission units pursuant to this Subpart and Subpart
E, F, G, H, I or M of this Part .
e)
The owner or operator of an emission unit that is subject to this Subpart and
Subpart E, F, G, H, I or M of this Part must operate such unit in a manner
consistent with good air pollution control practice to minimize NO
x
emissions.
(Source: Added at 33 Ill. Reg. _____, effective ______________)
Section 217.152 Compliance Date
a)
Compliance with the requirements of Subparts E, F, G, H, I and M by an owner or
operator of an emission unit that is subject to any of those Subparts is required
beginning January 1, 2012.
b)
Notwithstanding subsection (a) of this Section, compliance with the requirements
of Subpart G of this Part by an owner or operator of an emission unit subject to
Subpart G of this Part shall be extended until December 31, 2014, if such units are
required to meet emissions limitations for NOx, as measured using a continuous
emissions monitoring system, and included within a legally enforceable order on
or before December 31, 2009, whereby such emissions limitations are less than 30
percent of the emissions limitations set forth under Section 217.204.
c)
Notwithstanding subsection (a) of this Section, the owner or operator of emission
units subject to Subpart E or F of this Part and located at a petroleum refinery must
comply with the requirements of this Subpart and Subpart E or F of this Part, as
applicable, for those emission units beginning January 1, 2012, except that the
owner or operator of emission units listed in Appendix H must comply with the
requirements of this Subpart, including the option of demonstrating compliance
with the applicable Subpart through an emissions averaging plan under Section

102
217.158 and Subpart E or F of this Part, as applicable, for the listed emission units
beginning on the dates set forth in Appendix H. With Agency approval, the owner
or operator of emission units listed in Appendix H may elect to comply with the
requirements of this Subpart and Subpart E or F of this Part, as applicable, by
reducing the emissions of emission units other than those listed in Appendix H,
provided that the emissions limitations of such other emission units are equal to or
more stringent than the applicable emissions limitations set forth in Subpart E or F
of this Part, as applicable, by the dates set forth in Appendix H.
(Source: Added at 33 Ill. Reg. _____, effective ______________)
Section 217.154 Performance Testing
a)
Performance testing of NO
x
emissions for emission units constructed on or before
July 1, 2011, and subject to emissions limitations under Subpart E, F, G, H or I of
this Part must be conducted in accordance with Section 217.157 of this Subpart.
Except as provided for under Section 217.157(a)(4) and (e)(1), this This
subsection does not apply to owners and operators of emission units
demonstrating compliance through a continuous emissions monitoring system,
predictive emission monitoring system, or combustion tuning.
b)
Performance testing of NO
x
emissions for emission units for which construction
or modification occurs after July 1, 2011, and that are subject to emissions
limitations under Subpart E, F, G, H or I of this Part must be conducted within 60
days afterof achieving maximum operating rate but no later than 180 days after
initial startup of the new or modified emission unit, in accordance with Section
217.157 of this Subpart. Except as provided for under Section 217.157(a)(4) and
(e)(1), this This subsection does not apply to owners and operators of emission
units demonstrating compliance through a continuous emissions monitoring
system, predictive emission monitoring system, or combustion tuning.
c)
Notification of the initial startup of an emission unit subject to subsection (b) of
this Section must be provided to the Agency no later than 30 days after initial
startup.
d)
The owner or operator of an emission unit subject to subsection (a) or (b) of this
Section must notify the Agency of the scheduled date for the performance testing
in writing at least 30 days before such date and five days before such date.
e)
If demonstrating compliance through an emissions averaging plan, at least 30
days before changing the method of compliance, the owner or operator of an
emission unit must submit a written notification to the Agency describing the new
method of compliance, the reason for the change in the method of compliance,
and the scheduled date for performance testing, if required. Upon changing the
method of compliance, the owner or operator of an emission unit must submit to

103
the Agency a revised compliance certification that meets the requirements of
Section 217.155.
(Source: Added at 33 Ill. Reg. ____, effective ______________)
Section 217.155 Initial Compliance Certification
a)
By the applicable compliance date set forth under Section 217.152, an owner or
operator of an emission unit subject to Subpart E, F, G, H or I of this Part who is
not demonstrating compliance through the use of a continuous emissions
monitoring system must certify to the Agency that the emission unit will be in
compliance with the applicable emissions limitation of Subpart E, F, G, H or I of
this Part beginning on such applicable compliance date. The performance testing
certification must include the results of the performance testing performed in
accordance with Section 217.154(a) and (b) and the calculations necessary to
demonstrate that the subject emission unit will be in initial compliance.
b)
By the applicable compliance date set forth under Section 217.152, an owner or
operator of an emission unit subject to Subpart E, F, G, H, I or M of this Part who
is demonstrating compliance through the use of a continuous emissions
monitoring system must certify to the Agency that the affected emission units will
be in compliance with the applicable emissions limitation of Subpart E, F, G, H, I,
or M of this Part beginning on such applicable compliance date. The compliance
certification must include a certification of the installation and operation of a
continuous emissions monitoring system required under Section 217.157 and the
monitoring data necessary to demonstrate that the subject emission unit will be in
initial compliance.
(Source: Added at 33 Ill. Reg. ____, effective ______________)
Section 217.156 Recordkeeping and Reporting
a)
The owner or operator of an emission unit subject to Subpart E, F, G, H, I or M of
this Part must keep and maintain all records used to demonstrate initial
compliance and ongoing compliance with the requirements of those Subparts.
1)
Except as otherwise provided under this Subpart or Subpart E, F, G, H, I
or M of this Part, copies of such records must be submitted by the owner
or operator of the source to the Agency within 30 days after receipt of a
written request by the Agency.
2)
Such records must be kept at the source and maintained for at least five
years and must be available for immediate inspection and copying by the
Agency.

104
b)
The owner or operator of an emission unit subject to Subpart E, F, G, H, I or M of
this Part must maintain records that demonstrate compliance with the
requirements of those Subparts, as applicable, that include the following:
1)
Identification, type (e.g., gas-fired), and location of each unit.
2)
Calendar date of the record.
3)
Monthly, seasonal, and annual operating hours.
4)
Type and quantity of each fuel used monthly, seasonally, and annually.
5)
Product and material throughput, as applicable.
6)
Reports for all applicable emissions tests for NO
x
conducted on the unit,
including results.
7)
The date, time, and duration of any startup, shutdown, or malfunction in
the operation of any emission unit subject to Subpart E, F, G, H, I or M of
this Part or any emissions monitoring equipment. The records must
include a description of the malfunction and corrective maintenance
activity.
8)
A log of all maintenance and inspections related to the unit’s air pollution
control equipment for NO
x
that is performed on the unit.
9)
A log for the NO
x
monitoring device, if present, including periods when
not in service and maintenance and inspection activities that are performed
on the device.
10)
Identification of time periods for which operating conditions and pollutant
data were not obtained by the continuous emissions monitoring system,
including the reasons for not obtaining sufficient data and a description of
corrective actions taken.
11)
If complying with the emissions averaging plan provisions of Section
217.158, copies of the calculations used to demonstrate compliance with
the ozone season and annual control period limitations, noncompliance
reports for the ozone season, and ozone and annual control period
compliance reports submitted to the Agency.
c)
The owner or operator of an industrial boiler subject to Subpart E of this Part
must maintain records in order to demonstrate compliance with the combustion
tuning requirements under Section 217.166.

105
d)
The owner or operator of a process heater subject to Subpart F of this Part must
maintain records in order to demonstrate compliance with the combustion tuning
requirements under Section 217.186.
e)
The owner or operator of an emission unit subject to Subpart E, F, G, H, I or M of
this Part must maintain records in order to demonstrate compliance with the
testing and monitoring requirements under Section 217.157.
f)
The owner or operator of an emission unit subject to Subpart E, F, G, H or I of
this Part must provide the following information with respect to performance
testing pursuant to Section 217.157:
1)
Submit a testing protocol to the Agency at least 60 days prior to testing;
2)
Notify the Agency at least 30 days in writing prior to conducting
performance testing for NO
x
emissions and five days prior to such testing;
3)
Not later than 60 days after the completion of the test, submit the results of
the test to the Agency; and
4)
If, after the 30-days’ notice for an initially scheduled test is sent, there is a
delay (e.g., due to operational problems) in conducting the test as
scheduled, the owner or operator of the unit must notify the Agency as
soon as practicable of the delay in the original test date, either by
providing at least seven days’ prior notice of the rescheduled date of the
test or by arranging a new test date with the Agency by mutual agreement.
g)
The owner or operator of an emission unit subject to Subpart E, F, G, H, I or M of
this Part must notify the Agency of any exceedances of an applicable emissions
limitation of Subpart E, F, G, H, I or M of this Part by sending the applicable
report with an explanation of the causes of such exceedances to the Agency
within 30 days following the end of the applicable compliance period in which the
emissions limitation was not met.
h)
Within 30 days after the receipt of a written request by the Agency, the owner or
operator of an emission unit that is exempt from the requirements of Subpart E, F,
G, H, I or M of this Part must submit records that document that the emission unit
is exempt from those requirements to the Agency.
i)
If demonstrating compliance through an emissions averaging plan, by March 1
following the applicable calendar year, the owner or operator must submit to the
Agency a report that demonstrates the following:
1)
For all units that are part of the emissions averaging plan, the total mass of
allowable NOx emissions for the ozone season and for the annual control
period;

106
2)
The total mass of actual NOx emissions for the ozone season and annual
control period for each unit included in the averaging plan;
3)
The calculations that demonstrate that the total mass of actual NOx
emissions are less than the total mass of allowable NOx emissions using
equations in Section 217.158(f); and
4)
The information required to determine the total mass of actual NOx
emissions.
j)
The owner or operator of an emission unit subject to the requirements of Section
217.157 and demonstrating compliance through the use of a continuous emissions
monitoring system must submit to the Agency a report within 30 days after the
end of each calendar quarter. This report must include the following:
1)
Information identifying and explaining the times and dates when
continuous emissions monitoring for NO
x
was not in operation, other than
for purposes of calibrating or performing quality assurance or quality
control activities for the monitoring equipment; and
2)
An excess emissions and monitoring systems performance report in
accordance with the requirements of 40 CFR 60.7(c) and (d) and 60.13, or
40 CFR 75, or an alternate procedure approved by the Agency and
USEPA.
k)
The owner or operator of an emission unit subject to Subpart M of this Part must
comply with the compliance certification and recordkeeping and reporting
requirements in accordance with 40 CFR 96, or an alternate procedure approved
by the Agency and USEPA.
(Source: Added at 33 Ill. Reg. ____, effective ______________)
Section 217.157 Testing and Monitoring
a)
Industrial Boilers and Process Heaters
1)
The owner or operator of an industrial boiler subject to Subpart E of this
Part with a rated heat input capacity greater than 250 mmBtu/hr must
install, calibrate, maintain, and operate a continuous emissions monitoring
system on the emission unit for the measurement of NO
x
emissions
discharged into the atmosphere in accordance with 40 CFR 75, as
incorporated by reference in Section 217.104. However, the owner or
operator of an industrial boiler subject to Subpart E of this Part with a
rated heat input capacity greater than 250 mmBtu/hr that combusts blast
furnace gas with up to 10% natural gas on an annual basis and located at a

107
source that manufactures iron and steel is not required to install, calibrate,
maintain, and operate a continuous emissions monitoring system on such
industrial boiler, provided the heat input from natural gas does not exceed
10% on an annual basis and the owner or operator complies with the
performance test requirements under this Section and demonstrates, during
each performance test, that NO
x
emissions from such industrial boiler are
less than 70% of the applicable emissions limitation under Section
217.164. In the event such owner or operator is unable to meet the
requirements of this paragraph, a continuous emissions monitoring system
is required within 12 months of such event, or by December 31, 2012,
whichever is later.
2)
The owner or operator of an industrial boiler subject to Subpart E of this
Part with a rated heat input capacity greater than 100 mmBtu/hr but less
than or equal to 250 mmBtu/hr must install, calibrate, maintain, and
operate a continuous emissions monitoring system on such emission unit
for the measurement of NO
x
emissions discharged into the atmosphere in
accordance with 40 CFR 60, subpart A and appendix B, Performance
Specifications 2 and 3, and appendix F, Quality Assurance Procedures, as
incorporated by reference in Section 217.104.
3)
The owner or operator of a process heater subject to Subpart F of this Part
with a rated heat input capacity greater than 100 mmBtu/hr must install,
calibrate, maintain, and operate a continuous emissions monitoring system
on the emission unit for the measurement of NO
x
emissions discharged
into the atmosphere in accordance with 40 CFR 60, subpart A and
appendix B, Performance Specifications 2 and 3 and appendix F, Quality
Assurance Procedures, as incorporated by reference in Section 217.104.
4)
If demonstrating compliance through an emissions averaging plan, the
owner or operator of an industrial boiler subject to Subpart E of this Part,
or a process heater subject to Subpart F of this Part, with a rated heat input
capacity less than or equal to 100 mmBtu/hr and not demonstrating
compliance through a continuous emissions monitoring system must have
an initial performance test conducted pursuant to subsection (a)(4)(B) of
this Section and Section 217.154.
A)
An owner or operator of an industrial boiler or process heater must
have subsequent performance tests conducted pursuant to
subsection (a)(4)(B) of this Section at least once every five years.
When in the opinion of the Agency or USEPA, it is necessary to
conduct testing to demonstrate compliance with Section 217.164 or
217.184, as applicable, the owner or operator of an industrial boiler
or process heater must, at his or her own expense, have such test
conducted in accordance with the applicable test methods and

108
procedures specified in this Section within 90 days of receipt after
a notice to test from the Agency or USEPA.
B)
The owner or operator of an industrial boiler or process heater
must have a performance test conducted using 40 CFR 60, subpart
A and appendix A, Method 1, 2, 3, 4, 7E, or 19, as incorporated by
reference in Section 217.104, or other alternative USEPA methods
approved by the Agency. Each performance test must consist of
three separate runs, each lasting a minimum of 60 minutes. NO
x
emissions must be measured while the industrial boiler is operating
at maximum operating capacity or while the process heater is
operating at normal maximum load. If the industrial boiler or
process heater has combusted more than one type of fuel in the
prior year, a separate performance test is required for each fuel. If
a combination of fuels is typically used, a performance test may be
conducted, with Agency approval, on such combination of fuels
typically used. Except as provided under subsection (e) of this
Section, this subsection (a)(4)(B) does not apply if such owner or
operator is demonstrating compliance with an emissions limitation
through a continuous emissions monitoring system under
subsection (a)(1), (a)(2), (a)(3), or (a)(5) of this Section.
5)
Instead of complying with the requirements of subsections (a)(4),
(a)(4)(A), and (a)(4)(B) of this Section, an owner or operator of an
industrial boiler subject to Subpart E of this Part, or a process heater
subject to Subpart F of this Part, with a rated heat input capacity less than
or equal to 100 mmBtu/hr may install and operate a continuous emissions
monitoring system on such emission unit in accordance with the
applicable requirements of 40 CFR 60, subpart A and appendix B,
Performance Specifications 2 and 3 and appendix F, Quality Assurance
Procedures, as incorporated by reference in Section 217.104. The
continuous emissions monitoring system must be used to demonstrate
compliance with the applicable emissions limitation or emissions
averaging plan on an ozone season and annual basis.
6)
Notwithstanding subsection (a)(2) of this Section, the owner or operator of
an auxiliary boiler subject to Subpart E of this Part with a rated heat input
capacity less than or equal to 250 mmBtu/hr and a capacity factor of less
than or equal to 20% is not required to install, calibrate, maintain, and
operate a continuous emissions monitoring system on such boiler for the
measurement of NO
x
emissions discharged into the atmosphere, but must
comply with the performance test requirements under subsections (a)(4),
(a)(4)(A), and (a)(4)(B) of this Section.

109
b)
Glass Melting Furnaces; Cement Kilns; Lime Kilns; Iron and Steel Reheat,
Annealing, and Galvanizing Furnaces; and Aluminum Reverberatory and
Crucible Furnaces
1)
An owner or operator of a glass melting furnace subject to Subpart G of
this Part, cement kiln or lime kiln subject to Subpart H of this Part, iron
and steel reheat, annealing, or galvanizing furnace subject to Subpart I of
this Part, or aluminum reverberatory or crucible furnace subject to Subpart
H of this Part that has the potential to emit NO
x
in an amount equal to or
greater than one ton per day must install, calibrate, maintain, and operate a
continuous emissions monitoring system on such emission unit for the
measurement of NO
x
emissions discharged into the atmosphere in
accordance with 40 CFR 60, subpart A and appendix B, Performance
Specifications 2 and 3, and appendix F, Quality Assurance Procedures, as
incorporated by reference in Section 217.104.
2)
An owner or operator of a glass melting furnace subject to Subpart G of
this Part, cement kiln or lime kiln subject to Subpart H of this Part, iron
and steel reheat, annealing, or galvanizing furnace subject to Subpart I of
this Part, or aluminum reverberatory or crucible furnace subject to Subpart
I of this Part that has the potential to emit NO
x
in an amount less than one
ton per day must have an initial performance test conducted pursuant to
subsection (b)(4) of this Section and Section 217.154.
3)
An owner or operator of a glass melting furnace subject to Subpart G of
this Part, cement kiln or lime kiln subject to Subpart H of this Part, iron
and steel reheat, annealing, galvanizing furnace subject to Subpart I of this
Part, or aluminum reverberatory or crucible furnace subject to Subpart I of
this Part that has the potential to emit NO
x
in an amount less than one ton
per day must have subsequent performance tests conducted pursuant to
subsection (b)(4) of this Section as follows:
A)
For all glass melting furnaces subject to Subpart G of this Part,
cement kilns or lime kilns subject to Subpart H of this Part, iron
and steel reheat, annealing, or galvanizing furnace subject to
Subpart I of this Part, or aluminum reverberatory or crucible
furnaces subject to Subpart I of this Part, including all such units
included in an emissions averaging plan, at least once every five
years; and
B)
When, in the opinion of the Agency or USEPA, it is necessary to
conduct testing to demonstrate compliance with Section 217.204,
217.224, or 217.244, of this Part, as applicable, the owner or
operator of a glass melting furnace, cement kiln, lime kiln, iron and
steel reheat, annealing, or galvanizing furnace, or aluminum
reverberatory or crucible furnace must, at his or her own expense,

110
have such test conducted in accordance with the applicable test
methods and procedures specified in this Section within 90 days
after receipt of a notice to test from the Agency or USEPA.
4)
The owner or operator of a glass melting furnace, cement kiln, or lime kiln
must have a performance test conducted using 40 CFR 60, subpart A and
appendix A, Methods 1, 2, 3, 4, and 7E, as incorporated by reference in
Section 217.104 of this Part, or other alternative USEPA methods
approved by the Agency. The owner or operator of an iron and steel
reheat, annealing, or galvanizing furnace, or aluminum reverberatory or
crucible furnace must have a performance test conducted using 40 CFR
60, subpart A and appendix A, Method 1, 2, 3, 4, 7E, or 19, as
incorporated by reference in Section 217.104 of this Part, or other
alternative USEPA methods approved by the Agency. Each performance
test must consist of three separate runs, each lasting a minimum of 60
minutes. NO
x
emissions must be measured while the glass melting
furnace, cement kiln, lime kiln, iron and steel reheat, annealing, or
galvanizing furnace, or aluminum reverberatory or crucible furnace is
operating at maximum operating capacity. If the glass melting furnace,
cement kiln, lime kiln, iron and steel reheat, annealing, or galvanizing
furnace, or aluminum reverberatory or crucible furnace has combusted
more than one type of fuel in the prior year, a separate performance test is
required for each fuel. Except as provided under subsection (e) of this
Section, this subsection (b)(4) does not apply if such owner or operator is
demonstrating compliance with an emissions limitation through a
continuous emissions monitoring system under subsection (b)(1) or (b)(5)
of this Section.
5)
Instead of complying with the requirements of subsections (b)(2), (b)(3),
and (b)(4) of this Section, an owner or operator of a glass melting furnace
subject to Subpart G of this Part, cement kiln or lime kiln subject to
Subpart H of this Part, iron and steel reheat, annealing, or galvanizing
furnace subject to Subpart I of this Part, or aluminum reverberatory or
crucible furnace subject to Subpart I of this Part that has the potential to
emit NO
x
in an amount less than one ton per day may install and operate a
continuous emissions monitoring system on such emission unit in
accordance with the applicable requirements of 40 CFR 60, subpart A and
appendix B, Performance Specifications 2 and 3, and appendix F, Quality
Assurance Procedures, as incorporated by reference in Section 217.104 of
this Part. The continuous emissions monitoring system must be used to
demonstrate compliance with the applicable emissions limitation or
emissions averaging plan on an ozone season and annual basis.
c)
Fossil Fuel-Fired Stationary Boilers. The owner or operator of a fossil fuel-fired
stationary boiler subject to Subpart M of this Part must install, calibrate, maintain,
and operate a continuous emissions monitoring system on such emission unit for

111
the measurement of NO
x
emissions discharged into the atmosphere in accordance
with 40 CFR 96, subpart H.
d)
Common Stacks. If two or more emission units subject to Subpart E, F, G, H, I,
M, or Q of this Part are served by a common stack and the owner or operator of
such emission units is operating a continuous emissions monitoring system, the
owner or operator may, with written approval from the Agency, utilize a single
continuous emissions monitoring system for the combination of emission units
subject to Subpart E, F, G, H, I,M , or Q of this Part that share the common stack,
provided such emission units are subject to an emissions averaging plan under this
Part.
e)
Compliance with the continuous emissions monitoring system (CEMS)
requirements by an owner or operator of an emission unit who is required to
install, calibrate, maintain, and operate a CEMS on the emission unit under
subsection (a)(1), (a)(2), (a)(3), or (b)(1) of this Section, or who has elected to
comply with the CEMS requirements under subsection (a)(5) or (b)(5) of this
Section, or who has elected to comply with the predictive emission monitoring
system (PEMS) requirements under subsection (f) of this Section, is required by
the following dates:
1)
For the owner or operator of an emission unit that is subject to a
compliance date in calendar year 2012 under Section 217.152, compliance
with the CEMS or PEMS requirements, as applicable, under this Section
for such emission unit is required by December 31, 2012, provided that,
during the time between the compliance date and December 31, 2012, the
owner or operator must comply with the applicable performance test
requirements under this Section and the applicable recordkeeping and
reporting requirements under this Subpart. For the owner or operator of
an emission unit that is in compliance with the CEMS or PEMS
requirements, as applicable, under this Section on January 1, 2012, such
owner or operator is not required to comply with the performance test
requirements under this Section.
2)
For the owner or operator of an emission unit that is subject to a
compliance date in a calendar year other than calendar year 2012 under
Section 217.152 of this Subpart, compliance with the CEMS or PEMS
requirements, as applicable, under this Section for such emission unit is
required by the applicable compliance date, and such owner or operator is
not required to comply with the performance test requirements under this
Section.
f)
As an alternative to complying with the requirements of this Section, other than
the requirements under subsections (a)(1) and (c) of this Section, the owner or
operator of an emission unit who is not otherwise required by any other statute,
regulation, or enforceable order to install, calibrate, maintain, and operate a

112
CEMS on the emission unit may comply with the specifications and test
procedures for a predictive emission monitoring system (PEMS) on the emission
unit for the measurement of NO
x
emissions discharged into the atmosphere in
accordance with the requirements of 40 CFR 60, subpart A and appendix B,
Performance Specification 16. The PEMS must be used to demonstrate
compliance with the applicable emissions limitation or emissions averaging plan
on an ozone season and annual basis.
(Source: Added at 33 Ill. Reg. ____, effective ______________)
Section 217.158
Emissions Averaging Plans
a)
Notwithstanding any other emissions averaging plan provisions under this Part, an
owner or operator of a source with certain emission units subject to Subpart E, F,
G, H, I or M of this Part, or subject to Subpart Q of this Part that are located in
either one of the areas set forth under Section 217.150(a)(1)(A)(i) or (ii)
217.150(a)(1)(A) or (B), may demonstrate compliance with the applicable
Subpart through an emissions averaging plan. An emissions averaging plan can
only address emission units that are located at one source and each unit may only
be covered by one emissions averaging plan. Such emission units at the source
are affected units and are subject to the requirements of this Section.
1)
The following units may be included in an emissions averaging plan:
A)
Units that commenced operation on or before January 1, 2002.
B)
Units that the owner or operator may claim as exempt pursuant to
Section 217.162, 217.182, 217.202, 217.222, 217.242, or 217.342
of this Part, as applicable, but does not claim exempt. For as long
as such a unit is included in an emissions averaging plan, it will be
treated as an affected unit and subject to the applicable emissions
limitations, and testing, monitoring, recordkeeping and reporting
requirements.
C)
Units that commence operation after January 1, 2002, if the unit
replaces a unit that commenced operation on or before January 1,
2002, or it replaces a unit that replaced a unit that commenced
operation on or before January 1, 2002. The new unit must be
used for the same purpose and have substantially equivalent or less
process capacity or be permitted for less NO
x
emissions on an
annual basis than the actual NO
x
emissions of the unit or units that
are replaced. Within 90 days after permanently shutting down a
unit that is replaced, the owner or operator of such unit must
submit a written request to withdraw or amend the applicable
permit to reflect that the unit is no longer in service before the
replacement unit may be included in an emissions averaging plan.

113
2)
The following types of units may not be included in an emissions
averaging plan:
A)
Units that commence operation after January 1, 2002, except as
provided by subsection (a)(1)(C) of this Section.
B)
Units that the owner or operator is claiming are exempt pursuant to
Section 217.162, 217.182, 217.202, 217.222, 217.242, or 217.342
of this Part, as applicable.
C)
Units that are required to meet emission limits or control
requirements for NO
x,
as provided for in an enforceable order,
unless such order allows for emissions averaging. In the case of
petroleum refineries, this subsection does not prohibit including
industrial boilers or process heaters, or both, in an emissions
averaging plan where an enforceable order does not prohibit the
reductions made under such order from also being used for
compliance with any rules or regulations designed to address
regional haze or the non-attainment status of any area. Units that
are required to meet emission limits or control requirements for
NO
x
as provided for in an enforceable order, unless such order
allows for emissions averaging.
b)
An owner or operator must submit an emissions averaging plan to the Agency by
January 1, 2012. The plan must include, but is not limited to, the following:
1)
The list of affected units included in the plan by unit identification
number; and
2)
A sample calculation demonstrating compliance using the methodology
provided in subsection (f) of this Section for the ozone season (May 1
through September 30) and calendar year (January 1 through December
31).
c)
An owner or operator may amend an emissions averaging plan only once per
calendar year. Such an amended plan must be submitted to the Agency by
January 1 of the applicable calendar year. If an amended plan is not received by
the Agency by January 1 of the applicable calendar year, the previous year’s plan
will be the applicable emissions averaging plan.
d)
Notwithstanding subsection (c) of this Section:
1)
If a unit that is listed in an emissions averaging plan is taken out of
service, the owner or operator must submit to the Agency, within 30 days
after such occurrence, an updated emissions averaging plan; or

 
114
2)
If a unit that was exempt from the requirements of Subpart E, F, G, H, I,
or M of this Part pursuant to Section 217.162, 217.182, 217.202, 217.222,
217.242 or 217.342, of this Part, as applicable, no longer qualifies for an
exemption, the owner or operator may amend its existing averaging plan
to include such unit within 30 days after the unit no longer qualifies for the
exemption.
e)
An owner or operator must:
1)
Demonstrate compliance for the ozone season (May 1 through September
30) and the calendar year (January 1 through December 31) by using the
methodology and the units listed in the most recent emissions averaging
plan submitted to the Agency pursuant to subsection (b) of this Section,
the monitoring data or test data determined pursuant to Section 217.157,
and the actual hours of operation for the applicable averaging plan period;
and
2)
Submit to the Agency, by March 1 following each calendar year, a
compliance report containing the information required by Section
217.156(i).
f)
The total mass of actual NOx emissions from the units listed in the emissions
averaging plan must be equal to or less than the total mass of allowable NOx
emissions for those units for both the ozone season and calendar year. The
following equation must be used to determine compliance:
N
act
≤ N
all
Where:
N
act
=
=
n
i
act i j
k
1
j
( , )
=
1
EM
N
all
=
=
n
i
all i j
k
1
j
( , )
=
1
EM
N
act
=
Total sum of the actual NOx mass emissions from units
included in the averaging plan for each fuel used (tons per
ozone season and year).
N
all
=
Total sum of the allowable NOx mass emissions from units
included in the averaging plan for each fuel used (tons per
ozone season and year).
EM
act(i)
=
i
=
Subscript denoting an individual unit.
Total mass of actual NO
X
emissions in tons for a unit as
determined in subsection (f)(1) of this Section.
J
=
Subscript denoting the fuel type used.

 
115
K
=
Number of different fuel types.
n
=
Number of different units in the averaging plan.
EM
all(i)
=
Total mass of allowable NOx emissions in tons for a unit
as determined in subsection (f)(2) of this Section.
For each unit in the averaging plan, and each fuel used by such unit, determine
actual and allowable NOx emissions using the following equations:
1)
Actual emissions must be determined as follows:
When emission limits are prescribed in lb/mmBtu,
EM
act(i)
=
E
act(i)
x H
i
/2000
When emission limits are prescribed in lb/ton of processed
product,
EM
act(i)
=
E
act(i)
x P
i
/2000
2)
Allowable emissions must be determined as follows:
When emission limits are prescribed in lb/mmBtu,
EM
all(i)
=
E
all(i)
x H
i
/2000
When emission limits are prescribed in lb/ton of processed
product,
EM
all(i)
=
E
all(i)
x P
i
/2000
Where:
EM
act(i)
=
Total mass of actual NOx emissions in tons for a
unit.
EM
all(i)
=
Total mass of allowable NOx emissions in tons for
a unit.
E
act
=
Actual NOx emission rate (lbs/mmBtu or lbs/ton of
product) as determined by a performance test, a
continuous emissions monitoring system, or an
alternative method approved by the Agency.
E
all
=
Allowable NOx emission rate (lbs/mmBtu or lbs/ton
of product) as provided in Section 217.164,
217.184, 217.204, 217.224, 217.244, or 217.344, as
applicable. For an affected industrial boiler subject
to Subpart E of this Part, or process heater subject
to Subpart F of this Part, with a rated heat input
capacity less than or equal to 100 mmBtu/hr
demonstrating compliance through an emissions

116
averaging plan, the allowable NOx emission rate is
to be determined from a performance test after such
boiler or heater has undergone combustion tuning.
For all other units in an emissions averaging plan,
an uncontrolled NOx emission rate from USEPA’s
AP-42, as incorporated by reference in Section
217.104, or an uncontrolled NOx emission rate as
determined by an alternative method approved by
the Agency, will be used.
H
=
Heat input (mmBtu/ozone season or mmBtu/year)
calculated from fuel flow meter and the heating
value of the fuel used.
P
=
weight in tons of processed product.
g)
An owner or operator of an emission unit subject to Subpart Q of this Part that is
located in either one of the areas set forth under Section 217.150(a)(1)(A)(i) or (ii)
217.150(a)(1)(A) or (B) that is complying through an emissions averaging plan
under this Section must comply with the applicable provisions for determining
actual and allowable emissions under Section 217.390, the testing and monitoring
requirements under Section 217.394, and the recordkeeping and reporting
requirements under Section 217.396.
h)
The owner or operator of an emission unit located at a petroleum refinery who is
demonstrating compliance with an applicable Subpart through an emissions
averaging plan under this Section may exclude from the calculation demonstrating
compliance those time periods when an emission unit included in the emissions
averaging plan is shut down for a maintenance turnaround, provided that such
owner or operator notify the Agency in writing at least 30 days in advance of the
shutdown of the emission unit for the maintenance turnaround and the shutdown
of the emission unit does not exceed 45 days per ozone season or calendar year
and NO
x
pollution control equipment, if any, continues to operate on all other
emission units operating during the maintenance turnaround.
i)
The owner or operator of an emission unit that combusts a combination of coke
oven gas and other gaseous fuels and that is located at a source that manufactures
iron and steel who is demonstrating compliance with an applicable Subpart
through an emissions averaging plan under this Section may exclude from the
calculation demonstrating compliance those time periods when the coke oven gas
desulfurization unit included in the emissions averaging plan is shut down for
maintenance, provided that such owner or operator notify the Agency in writing at
least 30 days in advance of the shutdown of the coke oven gas desulfurization unit
for maintenance and such shutdown does not exceed 35 days per ozone season or
calendar year and NO
x
pollution control equipment, if any, continues to operate
on all other emission units operating during the maintenance period.

117
j)
The owner or operator of an emission unit located at a petroleum refinery who is
demonstrating compliance with an applicable Subpart through an emissions
averaging plan under this Section may exclude from the calculation demonstrating
compliance those time periods when NO
x
pollution control equipment that
controls one or more emission units included in the emissions averaging plan is
shut down for a maintenance turnaround, provided that such owner or operator
notify the Agency in writing at least 30 days in advance of the shutdown of the
NO
x
pollution control equipment for the maintenance turnaround and the
shutdown of the NO
x
pollution control equipment does not exceed 45 days per
ozone season or calendar year, and except for those emission units vented to the
NO
x
pollution control equipment undergoing the maintenance turnaround, NO
x
pollution control equipment, if any, continues to operate on all other emission
units operating during the maintenance turnaround.
(Source: Added at 33 Ill. Reg. ____, effective ______________)
SUBPART E: INDUSTRIAL BOILERS
Section 217.160 Applicability
a)
The provisions of Subpart D of this Part and this Subpart apply to all industrial
boilers located at sources subject to this Subpart pursuant to Section 217.150,
except as provided in subsections (b) and (c) of this Section.
b)
The provisions of this Subpart do not apply to boilers serving a generator that has
a nameplate capacity greater than 25 MWe and produces electricity for sale, and
cogeneration units, as that term is defined in 35 Ill. Adm. Code 225.130, if such
boilers meet the applicability criteria under Subpart M of Part 217or cogeneration
units are subject to the CAIR NO
x
Trading Programs under 35 Ill. Adm. Code
225.Subpart D or E.
c)
The provisions of this Subpart do not apply to fluidized catalytic cracking units,
their regenerator and associated CO boiler or boilers and CO furnace or furnaces
where present, if such units are located at a petroleum refinery and such units are
required to meet emission limits or control requirements for NO
x
as provided for
in an enforceable order.
(Source: Added at 33 Ill. Reg. ____, effective ______________)
Section 217.162 Exemptions
Notwithstanding Section 217.160 of this Subpart, the provisions of this Subpart do not apply to
an industrial boiler operating under a federally enforceable limit of NO
x
emissions from such
boiler to less than 15 tons per year and less than five tons per ozone season.

118
(Source: Added at 33 Ill. Reg. ____, effective ______________)
Section 217.164 Emissions Limitations
Except as provided for under Section 217.152, onOn and after January 1, 2012, no person shall
cause or allow emissions of NO
x
into the atmosphere from any industrial boiler to exceed the
following limitations. Compliance must be demonstrated with the applicable emissions
limitation on an ozone season and annual basis.
Fuel
Emission Unit Type and
Rated Heat Input Capacity
(mmmBtu/hr)
NO
x
Emissions
Limitation (lb/mmmBtu
or Requirement
a) Natural Gas or Other
Gaseous Fuels
1) Industrial boiler greater
than 100
0.08
2) Industrial boiler less than
equal to 100
Combustion tuning
b) Distillate Fuel Oil
1) Industrial boiler greater
than 100
0.10
2) Industrial boiler less than
or equal to 100
Combustion tuning
c) Other Liquid Fuels
1) Industrial boiler greater
than 100
0.15
2) Industrial boiler less than
or equal to 100
Combustion tuning
d) Solid Fuel
1) Industrial boiler greater
than 100, circulating
fluidized bed combustor
0.12
2) Industrial boiler greater
than 250
0.18
3) Industrial boiler greater
than 100 but less than or
equal to 250
0.25
4) Industrial boiler less than
or equal to 100
Combustion tuning

119
e)
For an industrial boiler combusting a combination of natural gas, coke oven gas,
and blast furnace gas, the NO
x
emissions limitation shall be calculated using the
following equation:
NO
x
emissions limitation for period in lb/MMBtu= (
NO
xNG
* Btu
NG
+
NOx
COG
* Btu
COG
+ NOx
BFG
* Btu
BFG
) /
(
Btu
NG
+ Btu
COG
+ Btu
BFG
)
Where:
NOx
NG
= 0.084 lb/MMBtu for natural gas
Btu
NG
= the heat input of natural gas in Btu over that period
NOx
COG
= 0.144 lb/MMBtu for coke oven gas
Btu
COG
= the heat input of coke oven gas in Btu over that period
NOx
BFG
= 0.0288 lb/MMBtu for blast furnace gas
Btu
BFG
= the heat input of blast furnace gas in Btu over that period
(Source: Added at 33 Ill. Reg. ____, effective _______)
Section 217.165 Combination of Fuel
s
The owner or operator of an industrial boiler subject to this Subpart and operated with any
combination of fuels must comply with a heat input weighted average emissions limitation to
demonstrate compliance with Section 217.164.
(Source: Added at 33 Ill. Reg. ____, effective ______________)
Section 217.166 Methods and Procedures for Combustion Tuning
The owner or operator of an industrial boiler subject to the combustion tuning requirements of
Section 217.164 must have combustion tuning performed on the boiler at least annually. The
combustion tuning must be performed by an employee of the owner or operator or a contractor
who has successfully completed a training course on the combustion tuning of boilers firing the
fuel or fuels that are fired in the boiler. The owner or operator must maintain the following
records that must be made available to the Agency upon request:
a)
The date the combustion tuning was performed;
b)
The name, title, and affiliation of the person who performed the combustion
tuning;

120
c)
Documentation demonstrating the provider of the combustion tuning training
course, the dates the training course was taken, and proof of successful
completion of the training course;
d)
Tune-up procedure followed and checklist of items (such as burners, flame
conditions, air supply, scaling on heating surface, etc.) inspected prior to the
actual tune-up; and
e)
Operating parameters recorded at the start and at conclusion of combustion
tuning.
(Source: Added at 33 Ill. Reg. ____, effective ______________)
SUBPART F: PROCESS HEATERS
Section 217.180 Applicability
The provisions of Subpart D of this Part and this Subpart apply to all process heaters located at
sources subject to this Subpart pursuant to Section 217.150.
(Source: Added at 33 Ill. Reg. ____, effective ______________)
Section 217.182 Exemptions
Notwithstanding Section 217.180, the provisions of this Subpart do not apply to a process heater
operating under a federally enforceable limit of NO
x
emissions from such heater to less than 15
tons per year and less than five tons per ozone season.
(Source: Added at 33 Ill. Reg. ____, effective ______________)
Section 217.184 Emissions Limitations
Except as provided for under Section 217.152, onOn and after January 1, 2012, no person shall
cause or allow emissions of NO
x
into the atmosphere from any process heater to exceed the
following limitations. Compliance must be demonstrated with the applicable emissions
limitation on an ozone season and annual basis.
Fuel
Emission Unit Type andRated
Heat Input Capacity(mmmBtu/hr)
NO
x
Emissions Limitation
(lb/mmmBtu
or Requirement
a) Natural Gas or
Other Gaseous
Fuels
1) Process heater greater
than 100
0.08
2) Process heater less than
Combustion tuning

121
or equal to 100
b) Residual Fuel
Oil
1) Process heater greater
than 100, natural draft
0.10
2) Process heater greater than
100, mechanical draft
0.15
3) Process heater less than
or equal to 100
Combustion tuning
c) Other Liquid
Fuels
1) Process heater greater
than 100, natural draft
0.05
2) Process heater greater than
100, mechanical draft
0.08
(Source: Added at 33 Ill. Reg. ____, effective ______________)
Section 217.185
Combination of Fuels
The owner or operator of a process heater subject to this Subpart and operated with any
combination of fuels must comply with a heat input weighted average emissions limitation to
demonstrate compliance with Section 217.184.
(Source: Added at 33 Ill. Reg. ____, effective ______________)
Section 217.186 Methods and Procedures for Combustion Tuning
The owner or operator of a process heater subject to the combustion tuning requirements of
Section 217.184 must have combustion tuning performed on the heater at least annually. The
combustion tuning must be performed by an employee of the owner or operator or a contractor
who has successfully completed a training course on the combustion tuning of heaters firing the
fuel or fuels that are fired in the heater. The owner or operator must maintain the following
records that must be made available to the Agency upon request:
a)
The date the combustion tuning was performed;
b)
The name, title, and affiliation of the person who performed the
combustion tuning;
c)
Documentation demonstrating the provider of the combustion tuning
training course, the dates the training course was taken, and proof of
successful completion of the training course;

122
d)
Tune-up procedure followed and checklist of items (such as burners, flame
conditions, air supply, scaling on heating surface, etc.) inspected prior to
the actual tune-up; and
e)
Operating parameters recorded at the start and at conclusion of
combustion tuning.
(Source: Added at 33 Ill. Reg. ____, effective ______________)
SUBPART G: GLASS MELTING FURNACES
Section 217.200 Applicability
The provisions of Subpart D of this Part and this Subpart apply to all glass melting furnaces
located at sources subject to this Subpart pursuant to Section 217.150.
(Source: Added at 33 Ill. Reg. ____, effective ______________)
Section 217.202 Exemptions
Notwithstanding Section 217.200, the provisions of this Subpart do not apply to a glass melting
furnace operating under a federally enforceable limit of NO
x
emissions from such furnace to less
than 15 tons per year and less than five tons per ozone season.
(Source: Added at 33 Ill. Reg. ____, effective ______________)
Section 217.204 Emissions Limitations
a)
On and after January 1, 2012, no person shall cause or allow emissions of NO
x
into the atmosphere from any glass melting furnace to exceed the following
limitations. Compliance must be demonstrated with the emissions limitation on
an ozone season and annual basis.
Product
Emission Unit Type
Nox Emissions Limitation
(lb/ton glass produced)
1) Container Glass
Glass melting furnace
5.0
2) Flat Glass
Glass melting furnace
7.9
3) Other Glass
Glass melting furnace
11.0
b)
The emissions during glass melting furnace startup (not to exceed 70 days) or
furnace idling (operation at less than 35% of furnace capacity) shall be excluded
from calculations for the purpose of demonstrating compliance with the seasonal
and annual emissions limitations under this Section, provided that such owner or

123
operator, at all times, including periods of startup and idling, to the extent
practicable, maintain and operate any affected emission unit including associated
air pollution control equipment in a manner consistent with good air pollution
control practice for minimizing emissions The owner or operator of a glass
melting furnace must maintain records that include the date, time, and duration of
any startup or idling in the operation of such glass melting furnace. The emissions
limitations under this Section do not apply during glass melting furnace startup
(not to exceed 70 days) or idling (operation at less than 35% of furnace capacity).
For the purposes of demonstrating seasonal and annual compliance, the emissions
limitation during such periods shall be calculated as follows:
NOx emissions limitation (lb/day) = (ANL) / (PPC)
Where:
ANL = The applicable NOx emissions limitation under this
Section in pounds per ton of glass produced
PPC = Permitted production capacity in tons of glass produced per
day
(Source: Added at 33 Ill. Reg. ____, effective ______________)
SUBPART H: CEMENT AND LIME KILNS
Section 217.220 Applicability
a)
Notwithstanding Subpart T of this Part, the provisions of Subpart D of this Part
and this Subpart apply to all cement kilns located at sources subject to this
Subpart pursuant to Section 217.150.
b)
The provisions of Subpart C of this Part and this Subpart apply to all lime kilns
located at sources subject to this Subpart pursuant to Section 217.150.
(Source: Added at 33 Ill. Reg. ____, effective ______________)
Section 217.222 Exemptions
Notwithstanding Section 217.220, the provisions of this Subpart do not apply to a cement kiln or
lime kiln operating under a federally enforceable limit of NO
x
emissions from such kiln to less
than 15 tons per year and less than five tons per ozone season.
(Source: Added at 33 Ill. Reg. ____, effective ______________)
Section 217.224 Emissions Limitations
a)
On and after January 1, 2012, no person shall cause or allow emissions of NO
x
into the atmosphere from any cement kiln to exceed the following limitations.

124
Compliance must be demonstrated with the applicable emissions limitation on an
ozone season and annual basis.
Emission Unit Type
Nox Emissions Limitation
(lb/ton clinker produced)
1)
Long dry kiln
5.1
2)
Short dry kiln
5.1
3)
Preheater kiln
3.8
4)
Preheater/precalciner kiln
2.8
b)
On and after January 1, 2012, no person shall cause or allow emissions of NO
x
into the atmosphere from any lime kiln to exceed the following limitations.
Compliance must be demonstrated with the applicable emissions limitation on an
ozone season and annual basis.
Fuel
Emission Unit Type
Nox Emissions Limitation
(lb/ton lime produced)
1) Gas
Rotary kiln
2.2
2) Coal
Rotary kiln
2.5
(Source: Added at 33 Ill. Reg. ____, effective ______________)
SUBPART I: IRON AND STEEL AND ALUMINUM MANUFACTURING
Section 217.240 Applicability
a)
The provisions of Subpart D of this Part and this Subpart apply to all reheat
furnaces, annealing furnaces, and galvanizing furnaces used in iron and steel
making located at sources subject to this Subpart pursuant to Section 217.150.
b)
The provisions of Subpart D of this Part and this Subpart apply to all
reverberatory furnaces and crucible furnaces used in aluminum melting located at
sources subject to this Subpart pursuant to Section 217.150.
(Source: Added at 33 Ill. Reg. ____, effective ______________)
Section 217.242 Exemptions
Notwithstanding Section 217.240, the provisions of this Subpart do not apply to an iron and steel
reheat furnace, annealing furnace, or galvanizing furnace, or aluminum reverberatory furnace or

125
crucible furnace operating under a federally enforceable limit of NO
x
emissions from such
furnace to less than 15 tons per year and less than five tons per ozone season.
(Source: Added at 33 Ill. Reg. ____, effective ______________)_________)
Section 217.244 Emissions Limitations
a)
On and after January 1, 2012, no person shall cause or allow emissions of NO
x
into the atmosphere from any reheat furnace annealing furnace, or galvanizing
furnace used in iron and steel making to exceed the following limitations.
Compliance must be demonstrated with the applicable emissions limitation on an
ozone season and annual basis.
No
x
Emissions Limitation
Emission Unit Type
(lb/mmBtu)_________
1)
Reheat furnace, regenerative
0.18
2)
Reheat recuperative, combusting
0.09
natural gas
3)
Reheat furnace, recuperative, combusting a
0.142
combination of natural gas and coke oven
gas
4)
Reheat furnace, cold-air
0.03
5)
Annealing furnace, regenerative
0.38
6)
Annealing furnace, recuperative
0.16
7)
Annealing furnace, cold-air
0.07
8)
Galvanizing furnace, regenerative
0.46
9)
Galvanizing furnace, cuperative
0.16
10)
Galvanizing furnace, cold-air
0.06
b)
On and after January 1, 2012, no person shall cause or allow emissions of NO
x
into the atmosphere from any reverberatory furnace or crucible furnace used in
aluminum melting to exceed the following limitations. Compliance must be
demonstrated with the applicable emissions limitation on an ozone season and
annual basis.

126
Emission Unit Type
NO
x
Emissions
Limitation (lb/mmmBtu)
1)
Reverberatory furnace
5.10.08
2)
Crucible furnace
5.10.16
(Source: Added at 33 Ill. Reg. ____, effective ______________)
SUBPART M: ELECTRICAL GENERATING UNITS
Section 217.340 Applicability
Notwithstanding Subpart V or W of this Part, the provisions of Subpart D of this Part and this
Subpart apply to any fossil fuel-fired stationary boiler serving at any time a generator that has a
nameplate capacity greater than 25 MWe and produces electricity for sale, excluding any units
listed in Appendix D of this Part, located at sources subject to this Subpart pursuant to Section
217.150.
(Source: Added at 33 Ill. Reg. ____, effective ______________)
Section 217.342 Exemptions
a)
Notwithstanding Section 217.340 , the provisions of this Subpart do not apply to a
fossil fuel-fired stationary boiler operating under a federally enforceable limit of
NO
x
emissions from such boiler to less than 15 tons per year and less than five
tons per ozone season.
b)
Notwithstanding Section 217.340, the provisions of this Subpart do not apply to a
coal-fired stationary boiler that commenced operation before January 1, 2008, that
is complying with Part35 Ill. Adm. Code 225.Subpart B through the multi-
pollutant standard under 35 Ill. Adm. Code 225.233 or the combined pollutant
standardstandards
under 35 Ill. Adm. Code 225.Subpart F.
(Source: Added at 33 Ill. Reg. ____, effective ______________)
Section 217.344 Emissions Limitations
On and after January 1, 2012, no person shall cause or allow emissions of NO
x
into the
atmosphere from any fossil fuel-fired stationary boiler to exceed the following limitations.
Compliance must be demonstrated with the applicable emissions limitation on an ozone season
and annual basis.
NO
x
Emissions
Fuel
Emission Unit Type
No
x
Emissions
Limitation (lb/mmmBtu)

127
a) Solid
Boiler
0.12
b) Natural gas
Boiler
0.06
c) Liquid
1) Boiler that commenced
operation before January 1,
2008.
0.10
2) Boiler that commenced
Operation on or after
January 1, 2008
0.08
(Source: Added at 33 Ill. Reg. ____, effective ______________)
Section 217.345 Combination of Fuels
The owner or operator of a fossil fuel-fired stationary boiler subject to this Subpart and operated
with any combination of fuels must comply with a heat input weighted average emissions
limitation to demonstrate compliance with Section 217.344.
(Source: Added at 33 Ill. Reg. ____, effective ______________)
Section 217.APPENDIX H: Compliance Dates for Certain Emission Units at Petroleum
Refineries
ExxonMobil Oil Corporation (Facility ID 197800AAA)
Point
Emission Unit Description
Compliance Date
0019
Crude Vacuum Heater (13-B-2)
December 31,2014
0038
Alky Iso-Stripper Reboiler (7-B-1)
December 31,2014
0033
CHD Charge Heater (3-B-1)
December 31,2014
0034
CHD Stripper Reboiler (3-B-2)
December 31,2014
0021
Coker East Charge Heater (16-B-1A)
December 31,2014
0021
Coker East Charge Heater (16-B-1B)
December 31,2014
0018
Crude Atmospheric Heater (1-B-1A)
December 31,2014
0018
Crude Atmospheric Heater (1-B-1B)
December 31,2014
ConocoPhillips Company Wood River Refinery (Facility ID 119090AAA)
Point
Emission Unit Description
Compliance Date
0017
BEU-HM-1
December 31, 2012
0018
BEU-HM-2
December 31, 2012
0004
CR-1 Feed Preheat, H-1
December 31, 2012
0005
CR-1 1st Interreactor Heater, H-2
December 31, 2012

128
0009
CR-1 3rd Interreactor Heater, H-7
December 31, 2012
0091
CR-3 Charge Heater
December 31, 2012
0092
CR-3 1st Reheat Heater, H-5
December 31, 2012
0082
Boiler 17
December 31, 2012
0080
Boiler 15
December 31, 2012
0073
Alky HM-2 Heater
December 31, 2012
0662
VF-4 Charge Heater, H-28
December 31, 2012
0664
DU-4 Charge Heater, H-24
December 31, 2014
0617
DCU Charge Heater, H-20
December 31, 2014
0014
HCU Fractionator Reboil, H-3
December 31, 2016
0024
DU-1 Primary Heater South, F-301
December 31, 2016
0025
DU-1 Secondary Heater North, F-302
December 31, 2016
0081
Boiler 16
December 31, 2016
0083
Boiler 18
December 31, 2016
0095
DHT Charge Heater
December 31, 2016
0028
DU-2 Lube Crude Heater F-200
December 31, 2016
0029
DU-2 Mixed Crude Heater West, F 202
December 31, 2016
0030
DU-2 Mixed Crude Heater East, F-203
December 31, 2016
0084
CR-2 North Heater
December 31, 2016
00170661 BEU-HM-1 CR-2 South Heater
December 31, 20162012
(Source: Added at 33 Ill. Reg. _____, effective __________)
IT IS SO ORDERED.
I, John T. Therriault, Assistant Clerk of the Illinois Pollution Control Board, certify that
the Board adopted the above opinion and order on July 23, 2009, by a vote of 5-0.
___________________________________
John T. Therriault, Assistant Clerk
Illinois Pollution Control Board

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