Approval and Promulgation of Implementation Plans; State of Montana; State Implementation Plan and Regional Haze Federal Implementation Plan, 29270-29271 [2012-11967]
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Federal Register / Vol. 77, No. 96 / Thursday, May 17, 2012 / Proposed Rules
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[FR Doc. 2012–11751 Filed 5–16–12; 8:45 am]
BILLING CODE 1410–72–P
VerDate Mar<15>2010
16:53 May 16, 2012
Jkt 226001
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 52
[EPA–R08–OAR–2011–0851, FRL–9673–6]
Approval and Promulgation of
Implementation Plans; State of
Montana; State Implementation Plan
and Regional Haze Federal
Implementation Plan
Environmental Protection
Agency.
ACTION: Proposed rule; corrections.
AGENCY:
EPA is correcting a proposed
rule that appeared in the Federal
Register on April 20, 2012. The
proposed rule includes the proposed
Federal Implementation Plan (FIP) to
address regional haze in the State of
Montana and the proposed approval of
revisions to the Montana SIP submitted
by the State of Montana through the
Montana Department of Environmental
Quality on February 17, 2012. We are
correcting some typographical errors
and clarifying some information with
this document.
FOR FURTHER INFORMATION CONTACT:
Vanessa Hinkle, EPA, Region 8, (303)
312–6561.
SUPPLEMENTARY INFORMATION:
Throughout this document, wherever
‘‘we’’ or ‘‘our’’ is used it means the EPA.
On April 20, 2012, EPA published the
proposed rule titled ‘‘Approval and
Promulgation of Implementation Plans;
State of Montana; State Implementation
Plan and Regional Haze Federal
Implementation Plan’’ (77 FR 23988).
See docket number EPA–R08–OAR–
2011–0851. The following corrections
are made to the proposed rule:
1. On page 23992, Footnote 7 is
amended to read as follows: ‘‘Guidance
for Estimating Natural Visibility
Conditions Under the Regional Haze
Rule, September 2003, EPA–454/B–03–
005, available at https://www.epa.gov/
ttncaaa1/t1/memoranda/rh_envcurhr_
gd.pdf, (hereinafter referred to as ‘‘our
2003 Natural Visibility Guidance’’); and
Guidance for Tracking Progress Under
the Regional Haze Rule, (September
2003, EPA–454/B–03–004, available at
https://www.epa.gov/ttncaaa1/t1/
memoranda/rh_tpurhr_gd.pdf,
(hereinafter referred to as our ‘‘2003
Tracking Progress Guidance’’).’’
2. On page 24002, Footnote 27 is
amended to read as follows:
‘‘ ‘‘Modeling Protocol: Montana Regional
Haze Federal Implementation Plan (FIP)
Support’’, University of North Carolina,
Contract EP–D–07–102, November 21,
2011.’’
SUMMARY:
PO 00000
Frm 00021
Fmt 4702
Sfmt 4702
3. On page 24004, Footnote 40 is
amended to read as follows: ‘‘Ash Grove
Update March 2012 (Ash Grove’s letter
indicates a mean of 14.4 lbs./ton clinker
and a 99th percentile of 18.6 lb NOX/ton
clinker. This is significantly greater than
the 2006 emissions shown in Table 10
for the Midlothian kilns.).’’
4. On pages 24013 and 24014,
Footnote 75 is amended to read as
follows: ‘‘BART analysis by Holcim for
Trident Cement Plant, Three Forks, MT
(‘‘Holcim Initial Response’’) (July 6,
2007); Responses to EPA comments on
BART analysis for Trident Cement Plant
(‘‘Holcim 2008 Responses’’) (Jan. 25,
2008); BART analysis by Holcim for low
NOX burners for Trident Cement Plant
(‘‘Holcim Additional Response, June
2009’’) (June 9, 2009); Response to EPA
letter regarding Confidential Business
Information (CBI) claims on BART
analysis for Trident Cement Plant
(‘‘Holcim Additional Response, August
2009’’) (Aug. 12, 2009); Response to
EPA request for NOX and SO2 emissions
data for 2008–2010 (‘‘Holcim 2011
Response’’) (June 30, 2011); Response to
EPA request for emissions and clinker
production for Holcim pursuant to CAA
section 114(a) (‘‘Holcim 2012
Response’’) (Mar. 2, 2012).’’
5. On page 24014, in the first column,
the first sentence of the second
paragraph is amended to read, ‘‘We
identified that the following previously
described NOX control technologies are
available: LNB, MKF, FGR, SNCR, and
SCR.’’
6. On page 24018, in Table 52, the
annual emissions reduction for fuel
switching option 2 is amended to 31.1
tpy, the remaining annual emissions for
fuel switching option 2 is amended to
19.1 tpy, the annual emissions
reduction for fuel switching option 1 is
amended to 16.1 tpy, and the remaining
annual emissions for fuel switching
option 1 is amended to 34.1 tpy.
7. On page 24020, in Table 60, the
emissions reductions from fuel
switching option 1 are amended to 16.1
tpy, the average cost effectiveness for
fuel switching option 1 is amended to
14,938 dollars per ton, the emissions
reduction from fuel switching option 2
is amended to 31.1 tpy, and the average
cost effectiveness for fuel switching
option 2 is amended to 21,211 dollars
per ton.
8. On page 24021, in Table 63, the
average cost effectiveness for fuel
switching option 2 is amended to 21,211
dollars per ton, and the average cost
effectiveness for fuel switching option 1
is amended to 14,938 dollars per ton.
9. On page 24023, Footnote 113 is
amended to read as follows: ‘‘Baseline
emissions were determined by averaging
E:\FR\FM\17MYP1.SGM
17MYP1
srobinson on DSK4SPTVN1PROD with PROPOSALS
Federal Register / Vol. 77, No. 96 / Thursday, May 17, 2012 / Proposed Rules
the annual emissions from 2008 through
2010 as reported to the CAMD database
available at https://camddataandmaps.
epa.gov/gdm/.’’
10. On page 24024, Footnote 123 is
amended to read as follows: ‘‘EPA’s
CCM Sixth Edition, January 2002, EPA/
452/B–02–001, Section 1, Chapter 2, p.
2–21.’’
11. On page 24025, Footnote 130 is
amended to read as follows: ‘‘ICAC
February 2008, p. 8.’’
12. On page 24031, Footnote 150 is
amended to read as follows: ‘‘Baseline
emissions were determined by averaging
the annual emissions from 2008 to 2010
as reported to the CAMD database
available at https://camddataandmaps.
epa.gov/gdm/.’’
13. On page 24059, in the first
column, the second paragraph is
amended to read, ‘‘We are eliminating
the four refineries from further
consideration as a result of consent
decrees entered into by the owners.
Under these consent decrees, emissions
have been reduced sufficiently after the
2002 baseline so that the Q/D for each
facility is below 10. Specifically,
ExxonMobil’s emissions in 2009 of NOX
and SO2 were 1,019 tpy, resulting in a
Q/D of 6. Cenex’s emissions in 2009 of
NOX and SO2 were 727 tpy, resulting in
a Q/D of 5. Conoco’s emissions in 2009
of NOX and SO2 were 1,087 tpy,
resulting in a Q/D of 8. Montana
Refining’s emissions in 2009 of NOX
and SO2 were 122 tpy, resulting in a Q/
D of 2. The consent decrees are available
in the docket.’’
14. On page 24063, in the first
column, the first sentence of the last
paragraph is amended to read, ‘‘We are
relying on CELP’s estimates that SCR
would take approximately 26 months to
install and that SNCR would take 16 to
24 weeks to install.239’’
15. On page 24064, the title for the
last column of Table 162 is amended to
read, ‘‘Remaining emissions (tpy).’’
16. On page 24070, in the third
column, the fourth sentence of the
second paragraph is amended to read,
‘‘This control option is functionally
equivalent to LSFO in terms of concept
and control efficiency.’’
17. On page 24071, in the first
column, the second full sentence of the
first paragraph is amended to read, ‘‘We
used 85% control for this analysis.’’
18. On page 24071, in the first
column, the sixth sentence of the
second paragraph is amended to read,
‘‘We used 70% control for this analysis
(about a 10% improvement over existing
controls).’’
19. On page 24074, in the third
column, the first sentence of the fifth
paragraph is amended to read, ‘‘We
VerDate Mar<15>2010
16:53 May 16, 2012
Jkt 226001
identified that the following
technologies to be available: extending
the Claus reaction into a lower
temperature liquid phase (the Sulfreen®
process) and tail gas scrubbing
(Wellman-Lord, SCOT, and traditional
FGD processes).’’
20. On page 24074, in the third
column, the first sentence of the sixth
paragraph is amended to read, ‘‘In the
Sulfreen® process, the Claus reaction is
extended at low temperatures (260 to
300 °F) to recover SO2 and H2S in the
tail gas.’’
21. On page 24075, in the third
column, the third paragraph is amended
to read, ‘‘Both the SCOT and Sulfreen®
processes are feasible; however, in the
BART Guidelines, EPA states that it may
be appropriate to eliminate from further
consideration technologies that provide
similar control levels at higher cost. See
70 FR 39165 (July 6, 2005). We think it
is appropriate to do the same for RP
determinations. In this case, Sulfreen®
systems reportedly can achieve 98% to
99.5% sulfur recovery efficiency while
SCOT can reportedly achieve sulfur
recovery as high as 99.8% to 99.9%. The
cost is higher for the Sulfreen® system
when compared to the SCOT process.
Because the SCOT process is more
effective and costs less than the
Sulfreen® system, the Sulfreen® system
was not considered further.’’
22. On page 24076, in the second
column, the first sentence of the third
paragraph is amended to read, ‘‘Plum
Creek Manufacturing’s Columbia Falls
Operation, in Columbia Falls, Montana
consists of a sawmill, a planer, and
plywood and medium density
fiberboard (MDF) processes.’’
23. On page 24097, the following
information is added to the third
column after the second paragraph, ‘‘K.
Congressional Review Act
The Congressional Review Act, 5
U.S.C. 801 et seq., as added by the Small
Business Regulatory Enforcement
Fairness Act of 1996, does not apply
because this action is not a ‘‘major rule’’
as defined by 5 U.S.C. 804(2).’’
24. On page 24097, in the third
column, under Subpart BB—Montana,
the first line of number three is
amended to read, ‘‘3. Add section
52.1395 to read as follows:’’ On page
24097, in the third column, under
Subpart BB—Montana, the first line of
number three is amended to read, ‘‘3.
Add section 52.1395 to read as follows:’’
25. On page 24098, section 52.1396
(c)(1) is amended to read, ‘‘The owners/
operators of EGUs subject to this section
shall not emit or cause to be emitted
PM, SO2 or NOX in excess of the
following limitations, in pounds per
million British thermal units (lb/
PO 00000
Frm 00022
Fmt 4702
Sfmt 4702
29271
MMBtu), averaged over a rolling 30-day
period for SO2 and NOX:’’
26. On page 24098, section 52.1396
(c)(2) is amended to read, ‘‘The owners/
operators of cement kilns subject to this
section shall not emit or cause to be
emitted PM, SO2 or NOX in excess of the
following limitations, in pounds per ton
of clinker produced, averaged over a
rolling 30-day period for SO2 and NOX:’’
27. On page 24099, the following is
added to section 52.1396 (g), ‘‘(5) All
particulate matter stack test results.’’
28. On page 24099, section 52.1396
(h)(4) is amended to read, ‘‘(4) Owner/
operator of each unit shall submit
results of any particulate matter stack
tests conducted for demonstrating
compliance win the particulate matter
BART limits in section (c) above, within
60 days after completion of the test.’’
29. On page 24100, section 52.1396
(h)(6) is amended to read, ‘‘(6) Any
other records required by 40 CFR part
60, Subpart F, or 40 CFR part 60,
Appendix F, Procedure 1.’’
30. On page 24100, section 52.1396
(i)(5) is added to read, ‘‘(5) Owner/
operator of each unit shall submit semiannual reports of any excursions under
the approved CAM plan in accordance
with the schedule specified in the
source’s title V permit.’’
List of Subjects in 40 CFR Part 52
Environmental protection, Air
pollution control, Intergovernmental
relations, Nitrogen dioxide, Particulate
matter, Reporting and recordkeeping
requirements, Sulfur oxides, Volatile
organic compounds.
Dated: May 8, 2012.
James B. Martin,
Regional Administrator, Region 8.
[FR Doc. 2012–11967 Filed 5–16–12; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 131
[EPA–HQ–OW–2009–0596; FRL–9670–7]
RIN 2040–AF41
Effective Date for the Water Quality
Standards for the State of Florida’s
Lakes and Flowing Waters
Environmental Protection
Agency (EPA).
ACTION: Proposed delay of effective date.
AGENCY:
The Environmental Protection
Agency (EPA) is proposing to extend the
July 6, 2012, effective date of the ‘‘Water
Quality Standards for the State of
Florida’s Lakes and Flowing Waters;
SUMMARY:
E:\FR\FM\17MYP1.SGM
17MYP1
Agencies
[Federal Register Volume 77, Number 96 (Thursday, May 17, 2012)]
[Proposed Rules]
[Pages 29270-29271]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2012-11967]
=======================================================================
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 52
[EPA-R08-OAR-2011-0851, FRL-9673-6]
Approval and Promulgation of Implementation Plans; State of
Montana; State Implementation Plan and Regional Haze Federal
Implementation Plan
AGENCY: Environmental Protection Agency.
ACTION: Proposed rule; corrections.
-----------------------------------------------------------------------
SUMMARY: EPA is correcting a proposed rule that appeared in the Federal
Register on April 20, 2012. The proposed rule includes the proposed
Federal Implementation Plan (FIP) to address regional haze in the State
of Montana and the proposed approval of revisions to the Montana SIP
submitted by the State of Montana through the Montana Department of
Environmental Quality on February 17, 2012. We are correcting some
typographical errors and clarifying some information with this
document.
FOR FURTHER INFORMATION CONTACT: Vanessa Hinkle, EPA, Region 8, (303)
312-6561.
SUPPLEMENTARY INFORMATION: Throughout this document, wherever ``we'' or
``our'' is used it means the EPA.
On April 20, 2012, EPA published the proposed rule titled
``Approval and Promulgation of Implementation Plans; State of Montana;
State Implementation Plan and Regional Haze Federal Implementation
Plan'' (77 FR 23988). See docket number EPA-R08-OAR-2011-0851. The
following corrections are made to the proposed rule:
1. On page 23992, Footnote 7 is amended to read as follows:
``Guidance for Estimating Natural Visibility Conditions Under the
Regional Haze Rule, September 2003, EPA-454/B-03-005, available at
https://www.epa.gov/ttncaaa1/t1/memoranda/rh_envcurhr_gd.pdf,
(hereinafter referred to as ``our 2003 Natural Visibility Guidance'');
and Guidance for Tracking Progress Under the Regional Haze Rule,
(September 2003, EPA-454/B-03-004, available at https://www.epa.gov/ttncaaa1/t1/memoranda/rh_tpurhr_gd.pdf, (hereinafter referred to as
our ``2003 Tracking Progress Guidance'').''
2. On page 24002, Footnote 27 is amended to read as follows: ``
``Modeling Protocol: Montana Regional Haze Federal Implementation Plan
(FIP) Support'', University of North Carolina, Contract EP-D-07-102,
November 21, 2011.''
3. On page 24004, Footnote 40 is amended to read as follows: ``Ash
Grove Update March 2012 (Ash Grove's letter indicates a mean of 14.4
lbs./ton clinker and a 99th percentile of 18.6 lb NOX/ton
clinker. This is significantly greater than the 2006 emissions shown in
Table 10 for the Midlothian kilns.).''
4. On pages 24013 and 24014, Footnote 75 is amended to read as
follows: ``BART analysis by Holcim for Trident Cement Plant, Three
Forks, MT (``Holcim Initial Response'') (July 6, 2007); Responses to
EPA comments on BART analysis for Trident Cement Plant (``Holcim 2008
Responses'') (Jan. 25, 2008); BART analysis by Holcim for low
NOX burners for Trident Cement Plant (``Holcim Additional
Response, June 2009'') (June 9, 2009); Response to EPA letter regarding
Confidential Business Information (CBI) claims on BART analysis for
Trident Cement Plant (``Holcim Additional Response, August 2009'')
(Aug. 12, 2009); Response to EPA request for NOX and
SO2 emissions data for 2008-2010 (``Holcim 2011 Response'')
(June 30, 2011); Response to EPA request for emissions and clinker
production for Holcim pursuant to CAA section 114(a) (``Holcim 2012
Response'') (Mar. 2, 2012).''
5. On page 24014, in the first column, the first sentence of the
second paragraph is amended to read, ``We identified that the following
previously described NOX control technologies are available:
LNB, MKF, FGR, SNCR, and SCR.''
6. On page 24018, in Table 52, the annual emissions reduction for
fuel switching option 2 is amended to 31.1 tpy, the remaining annual
emissions for fuel switching option 2 is amended to 19.1 tpy, the
annual emissions reduction for fuel switching option 1 is amended to
16.1 tpy, and the remaining annual emissions for fuel switching option
1 is amended to 34.1 tpy.
7. On page 24020, in Table 60, the emissions reductions from fuel
switching option 1 are amended to 16.1 tpy, the average cost
effectiveness for fuel switching option 1 is amended to 14,938 dollars
per ton, the emissions reduction from fuel switching option 2 is
amended to 31.1 tpy, and the average cost effectiveness for fuel
switching option 2 is amended to 21,211 dollars per ton.
8. On page 24021, in Table 63, the average cost effectiveness for
fuel switching option 2 is amended to 21,211 dollars per ton, and the
average cost effectiveness for fuel switching option 1 is amended to
14,938 dollars per ton.
9. On page 24023, Footnote 113 is amended to read as follows:
``Baseline emissions were determined by averaging
[[Page 29271]]
the annual emissions from 2008 through 2010 as reported to the CAMD
database available at https://camddataandmaps.epa.gov/gdm/.''
10. On page 24024, Footnote 123 is amended to read as follows:
``EPA's CCM Sixth Edition, January 2002, EPA/452/B-02-001, Section 1,
Chapter 2, p. 2-21.''
11. On page 24025, Footnote 130 is amended to read as follows:
``ICAC February 2008, p. 8.''
12. On page 24031, Footnote 150 is amended to read as follows:
``Baseline emissions were determined by averaging the annual emissions
from 2008 to 2010 as reported to the CAMD database available at https://
camddataandmaps.epa.gov/gdm/.''
13. On page 24059, in the first column, the second paragraph is
amended to read, ``We are eliminating the four refineries from further
consideration as a result of consent decrees entered into by the
owners. Under these consent decrees, emissions have been reduced
sufficiently after the 2002 baseline so that the Q/D for each facility
is below 10. Specifically, ExxonMobil's emissions in 2009 of
NOX and SO2 were 1,019 tpy, resulting in a Q/D of
6. Cenex's emissions in 2009 of NOX and SO2 were
727 tpy, resulting in a Q/D of 5. Conoco's emissions in 2009 of
NOX and SO2 were 1,087 tpy, resulting in a Q/D of
8. Montana Refining's emissions in 2009 of NOX and
SO2 were 122 tpy, resulting in a Q/D of 2. The consent
decrees are available in the docket.''
14. On page 24063, in the first column, the first sentence of the
last paragraph is amended to read, ``We are relying on CELP's estimates
that SCR would take approximately 26 months to install and that SNCR
would take 16 to 24 weeks to install.\239\''
15. On page 24064, the title for the last column of Table 162 is
amended to read, ``Remaining emissions (tpy).''
16. On page 24070, in the third column, the fourth sentence of the
second paragraph is amended to read, ``This control option is
functionally equivalent to LSFO in terms of concept and control
efficiency.''
17. On page 24071, in the first column, the second full sentence of
the first paragraph is amended to read, ``We used 85% control for this
analysis.''
18. On page 24071, in the first column, the sixth sentence of the
second paragraph is amended to read, ``We used 70% control for this
analysis (about a 10% improvement over existing controls).''
19. On page 24074, in the third column, the first sentence of the
fifth paragraph is amended to read, ``We identified that the following
technologies to be available: extending the Claus reaction into a lower
temperature liquid phase (the Sulfreen[supreg] process) and tail gas
scrubbing (Wellman-Lord, SCOT, and traditional FGD processes).''
20. On page 24074, in the third column, the first sentence of the
sixth paragraph is amended to read, ``In the Sulfreen[supreg] process,
the Claus reaction is extended at low temperatures (260 to 300 [deg]F)
to recover SO2 and H2S in the tail gas.''
21. On page 24075, in the third column, the third paragraph is
amended to read, ``Both the SCOT and Sulfreen[supreg] processes are
feasible; however, in the BART Guidelines, EPA states that it may be
appropriate to eliminate from further consideration technologies that
provide similar control levels at higher cost. See 70 FR 39165 (July 6,
2005). We think it is appropriate to do the same for RP determinations.
In this case, Sulfreen[supreg] systems reportedly can achieve 98% to
99.5% sulfur recovery efficiency while SCOT can reportedly achieve
sulfur recovery as high as 99.8% to 99.9%. The cost is higher for the
Sulfreen[supreg] system when compared to the SCOT process. Because the
SCOT process is more effective and costs less than the Sulfreen[supreg]
system, the Sulfreen[supreg] system was not considered further.''
22. On page 24076, in the second column, the first sentence of the
third paragraph is amended to read, ``Plum Creek Manufacturing's
Columbia Falls Operation, in Columbia Falls, Montana consists of a
sawmill, a planer, and plywood and medium density fiberboard (MDF)
processes.''
23. On page 24097, the following information is added to the third
column after the second paragraph, ``K. Congressional Review Act
The Congressional Review Act, 5 U.S.C. 801 et seq., as added by the
Small Business Regulatory Enforcement Fairness Act of 1996, does not
apply because this action is not a ``major rule'' as defined by 5
U.S.C. 804(2).''
24. On page 24097, in the third column, under Subpart BB--Montana,
the first line of number three is amended to read, ``3. Add section
52.1395 to read as follows:'' On page 24097, in the third column, under
Subpart BB--Montana, the first line of number three is amended to read,
``3. Add section 52.1395 to read as follows:''
25. On page 24098, section 52.1396 (c)(1) is amended to read, ``The
owners/operators of EGUs subject to this section shall not emit or
cause to be emitted PM, SO2 or NOX in excess of
the following limitations, in pounds per million British thermal units
(lb/MMBtu), averaged over a rolling 30-day period for SO2
and NOX:''
26. On page 24098, section 52.1396 (c)(2) is amended to read, ``The
owners/operators of cement kilns subject to this section shall not emit
or cause to be emitted PM, SO2 or NOX in excess
of the following limitations, in pounds per ton of clinker produced,
averaged over a rolling 30-day period for SO2 and
NOX:''
27. On page 24099, the following is added to section 52.1396 (g),
``(5) All particulate matter stack test results.''
28. On page 24099, section 52.1396 (h)(4) is amended to read, ``(4)
Owner/operator of each unit shall submit results of any particulate
matter stack tests conducted for demonstrating compliance win the
particulate matter BART limits in section (c) above, within 60 days
after completion of the test.''
29. On page 24100, section 52.1396 (h)(6) is amended to read, ``(6)
Any other records required by 40 CFR part 60, Subpart F, or 40 CFR part
60, Appendix F, Procedure 1.''
30. On page 24100, section 52.1396 (i)(5) is added to read, ``(5)
Owner/operator of each unit shall submit semi-annual reports of any
excursions under the approved CAM plan in accordance with the schedule
specified in the source's title V permit.''
List of Subjects in 40 CFR Part 52
Environmental protection, Air pollution control, Intergovernmental
relations, Nitrogen dioxide, Particulate matter, Reporting and
recordkeeping requirements, Sulfur oxides, Volatile organic compounds.
Dated: May 8, 2012.
James B. Martin,
Regional Administrator, Region 8.
[FR Doc. 2012-11967 Filed 5-16-12; 8:45 am]
BILLING CODE 6560-50-P