[Federal Register: October 11, 2007 (Volume 72, Number 196)]
[Rules and Regulations]
[Page 57858]
[DOCID:fr11oc07-8]

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DEPARTMENT OF HOMELAND SECURITY

Coast Guard

33 CFR Part 117

[CGD01-07-137]

Drawbridge Operation Regulations; Jamaica Bay, New York, NY

AGENCY: Coast Guard, DHS.

ACTION: Notice of temporary deviation from regulations.

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SUMMARY: The Commander, First Coast Guard District, has issued a
temporary deviation from the regulation governing the operation of the
Beach Channel Railroad Bridge across Jamaica Bay, mile 6.7, at New
York, New York. Under this temporary deviation the Beach Channel
Railroad Bridge may remain in the closed position on Saturday and
Sunday from 6 a.m. to 9 p.m., on October 13, 14, 20, and 21, 2007. This
deviation is necessary to facilitate bridge track repairs.

DATES: This deviation is effective from October 13, 2007 through
October 21, 2007.

ADDRESSES: Materials referred to in this document are available for
inspection or copying at the First Coast Guard District, Bridge Branch
Office, 408 Atlantic Avenue, Boston, Massachusetts, 02110, between 7
a.m. and 3 p.m., Monday through Friday, except Federal holidays. The
telephone number is<PHONE_NUMBER>. The First Coast Guard District
Bridge Branch Office maintains the public docket for this temporary
deviation.

FOR FURTHER INFORMATION CONTACT: Judy Leung-Yee, Project Officer, First
Coast Guard District, at<PHONE_NUMBER>.

SUPPLEMENTARY INFORMATION: The Beach Channel Railroad Bridge, across
Jamaica Bay, mile 6.7, at New York, New York, has a vertical clearance
in the closed position of 26 feet at mean high water and 31 feet at
mean low water. The existing drawbridge operation regulations are
listed at 33 CFR 117.5.
    The owner of the bridge, New York City Transit Authority, requested
a temporary deviation to complete repairs to the bridge rails.
    Under this temporary deviation, in effect for two weekends, the
Beach Channel Railroad Bridge need not open for the passage of vessel
traffic on Saturday and Sunday between 6 a.m. and 9 p.m. on October 13,
14, 20, and 21, 2007.
    In accordance with 33 CFR 117.35(e), the bridge must return to its
regular operating schedule immediately at the end of the designated
time period. This deviation from the operating regulations is
authorized under 33 CFR 117.35.
    Should the bridge maintenance authorized by this temporary
deviation be completed before the end of the effective period published
in this notice, the Coast Guard will rescind the remainder of this
temporary deviation, and the bridge shall be returned to its normal
operation schedule. Notice of the above action shall be provided to the
public in the Local Notice to Mariners and the Federal Register, where
practicable.

    Dated: September 28, 2007.
Gary Kassof,
Bridge Program Manager, First Coast Guard District.
 [FR Doc. E7-20009 Filed 10-10-07; 8:45 am]

BILLING CODE 4910-15-P


[Federal Register Volume 85, Number 131 (Wednesday, July 8, 2020)]
[Proposed Rules]
[Pages 40951-40958]
[FR Doc No: 2020-14360]

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ENVIRONMENTAL PROTECTION AGENCY

40 CFR Part 52

[EPA-R06-OAR-2018-0856; FRL-10011-09-Region 6]

Air Plan Approval; New Mexico; Repeal of State Regulations for
Particulate Matter for Lime Manufacturing Plants

AGENCY: Environmental Protection Agency (EPA).

ACTION: Proposed rule.

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SUMMARY: Pursuant to the Federal Clean Air Act (CAA or the Act), the
Environmental Protection Agency (EPA) is proposing to approve a New
Mexico State Implementation Plan (SIP) revision for the repeal of State
regulations titled 20.2.20 NMAC (Title 20: Environmental Protection,
Chapter 2: Air Quality (Statewide), Part 20: Lime Manufacturing
Plants--Particulate Matter of the New Mexico Administrative Code) that
cover particulate matter emission standards for lime manufacturing
plants and lime hydrators in the State of New Mexico. EPA is proposing
to approve the repeal of the regulations based on the CAA section
110(l) demonstration contained in the New Mexico submittal, which
provides that the SIP revision will not interfere with attainment and
maintenance of the NAAQS or any other CAA requirement.

DATES: Written comments must be received on or before August 7, 2020.

ADDRESSES: Submit your comments, identified by Docket No. EPA-R06-OAR-
2018-0856, at https://www.regulations.gov or via email to<EMAIL_ADDRESS>Follow the online instructions for submitting
comments. Once submitted, comments cannot be edited or removed from
Regulations.gov. The EPA may publish any comment received to its public
docket. Do not submit electronically any information you consider to be
Confidential Business Information (CBI) or other information whose
disclosure is restricted by statute. Multimedia submissions (audio,
video, etc.) must be accompanied by a written comment. The written
comment is considered the official comment and should include
discussion of all points you wish to make. The EPA will generally not
consider comments or comment contents located outside of the primary
submission (i.e. on the web, cloud, or other file sharing system). For
additional submission methods, please contact Ms. Karolina Ruan Lei,
(214) 665-7346<EMAIL_ADDRESS>For the full EPA public
comment policy, information about CBI or multimedia submissions, and
general guidance on making effective comments, please visit https://www.epa.gov/dockets/commenting-epa-dockets.
    Docket: The index to the docket for this action is available
electronically at www.regulations.gov. While all documents in the
docket are listed in the index, some information may not be publicly
available due to docket file size restrictions or content (e.g., CBI).

FOR FURTHER INFORMATION CONTACT: Ms. Karolina Ruan Lei,<PHONE_NUMBER>,
<EMAIL_ADDRESS>Out of an abundance of caution for members
of the public and our staff, the EPA Region 6 office will be closed to
the public to reduce the risk of transmitting COVID-19. We encourage
the public to submit comments via https://www.regulations.gov, as there
will be a delay in processing mail and no courier or hand deliveries
will be accepted. Please call or email the contact listed above if you
need alternative access to material indexed but not provided in the
docket.

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

Table of Contents

I. Background
    A. Clean Air Act Section 110(l)
    B. State Implementation Plans (SIPs)
    C. The National Ambient Air Quality Standards (NAAQS)
    D. History of Reviews of the NAAQS for Particulate Matter
II. New Mexico's Submittal
    A. The Regulation Proposed for Repeal

    B. Particulate Matter Designated Areas in New Mexico
    C. Affected Facilities
III. The EPA's Evaluation of the State's Submittal and
Noninterference Demonstration
    A. Potential Impact on Emissions
    B. Air Quality Modeling Demonstration for Lhoist North America
    C. Air Monitoring Data for New Mexico
    D. Summary of EPA's Evaluation
IV. Proposed Action
V. Statutory and Executive Order Reviews

I. Background

A. Clean Air Act Section 110(l)

    Section 110(l) of the Clean Air Act (CAA) provides that ``. . . The
Administrator shall not approve a revision of a plan if the revision
would interfere with any applicable requirement concerning attainment
and reasonable further progress (as defined in [CAA section 171]) or
any other applicable requirement of [the CAA].'' 42 U.S.C. 7410(l).
Section 110(l) applies to all requirements of the CAA and to all areas
of the country, whether attainment, nonattainment, unclassifiable or
maintenance for one or more of the six criteria pollutants. Section
110(l) applies to all NAAQS that are in effect, including those for
which SIP submissions have not been made and addresses any interference
with CAA requirements that would occur as a result from a SIP revision.
In general, the level of rigor needed for any CAA section 110(l)
demonstration will vary depending on the nature of the revision.
    Additionally, a state may substitute equivalent emissions
reductions to compensate for any change to a plan to ensure actual
emissions to the air are not increased and thus preserve status quo air
quality. ``Equivalent'' emissions reductions are reductions that are
equal to or greater than those reductions achieved by the control
measure approved into the plan. To show that compensating emissions
reductions are equivalent, adequate justification must be provided. The
compensating, equivalent reductions should represent actual emissions
reductions achieved in a contemporaneous time frame to the change of
the existing control measure in order to preserve the status quo air
quality. If the status quo is preserved, noninterference is
demonstrated. In addition to being contemporaneous, the equivalent
emissions reductions should also be permanent, enforceable,
quantifiable, and surplus.
    Each noninterference demonstration submitted by a state requesting
a SIP revision is evaluated on a case-by-case basis, considering the
circumstances of the revision. EPA may approve a noninterference
demonstration based on an evaluation of the SIP revision on air quality
and/or the information provided in the noninterference demonstration.
    Some control measures may not be removed from a SIP even if doing
so would not interfere with the CAA's air quality goals. These measures
are often referred to as ``mandatory'' measures because the CAA
requires that they be included in the SIP for an area based on the
area's designation status and classification. Measures not tied to an
area's classification and not mandated by the CAA are often referred to
as ``discretionary'' measures. States can remove discretionary measures
from an attainment, nonattainment or maintenance plan. However, a
section 110(l) demonstration of noninterference would still be
required.

B. State Implementation Plans (SIPs)

    A SIP is a set of statutes, air pollution regulations, control
strategies, other means or techniques, and technical analyses developed
by the state to ensure that the state meets the NAAQS. The SIP is
required by section 110 and other provisions of the CAA. These SIPs can
be extensive, containing state regulations or other enforceable
documents and supporting information such as emissions inventories,
monitoring networks, and modeling demonstrations. Each state must
submit these regulations and control strategies to EPA for approval and
incorporation into the federally enforceable SIP. Each federally
approved SIP protects air quality primarily by addressing air pollution
at its point of origin.

C. The National Ambient Air Quality Standards (NAAQS)

    Section 108 of the CAA requires EPA to establish NAAQS for
pollutants that ``may reasonably be anticipated to endanger public
health and welfare,'' and to develop a primary and secondary standard
for each NAAQS. The primary standard is designed to protect human
health with an adequate margin of safety, and the secondary standard is
designed to protect public welfare and the environment. EPA has set
NAAQS for six common air pollutants, referred to as criteria
pollutants. These pollutants are: Carbon monoxide, lead, nitrogen
dioxide, ozone, particulate matter, and sulfur dioxide. These standards
present state and local governments with the minimum air quality levels
they must meet to comply with the CAA. Additionally, these standards
provide information to residents of the United States about the quality
of the air in their communities.

D. History of Reviews of the NAAQS for Particulate Matter

    Section 109 of the CAA requires EPA to complete a thorough review
of the NAAQS every five years and make such revisions in such criteria
and standards as may be appropriate. On April 30, 1971, EPA promulgated
the first NAAQS for particulate matter with the indicator set to total
suspended particulate (TSP) (36 FR 8186). TSP was measured by the EPA
reference method in 40 CFR part 50, Appendix B. The primary TSP
standards were set at 260 micrograms per cubic meter of air ([mu]g/
m\3\) averaged over a 24-hour period, not to be exceeded more than once
per year, and 75 [mu]g/m\3\ annual geometric mean, while the secondary
TSP standards were set to 150 [mu]g/m\3\ for the 24-hour average and 60
[mu]g/m\3\ for the annual mean.
    On July 1, 1987, the EPA published revisions to the NAAQS for
particulate matter (52 FR 24634). The principle revisions to the 1971
NAAQS included replacing TSP as the indicator for the ambient standards
with a new indicator that includes particles with an aerodynamic
diameter less than or equal to a nominal 10 [mu]m (PM10, or
coarse particulate matter), replacing the 24-hour primary TSP standard
with a 24-hour PM10 standard of 150 [mu]g/m\3\, replacing
the annual primary TSP standard with an annual PM10 standard
of 50 [mu]g/m\3\, and replacing the secondary TSP standard with 24-hour
and annual PM10 standards identical in all respects to the
primary standards.
    On July 18, 1997, the EPA promulgated a new NAAQS for fine
particulate matter (PM2.5), which were defined as particles
with an aerodynamic diameter less than or equal to a nominal 2.5 [mu]m
(62 FR 38652). EPA promulgated a 24-hour and an annual standard for
PM2.5. For the 1997 particulate matter NAAQS, the annual
PM2.5 standard was set to 15 [mu]g/m\3\ and the 24-hour
standard was set to 65 [mu]g/m\3\. On October 17, 2006, EPA published
revised standards for particulate matter (71 FR 61144). For
PM2.5, the annual standard of 15 [mu]g/m\3\ was retained,
and the 24-hour standard was revised to 35 [mu]g/m\3\. For
PM10, the annual standard of 50 [mu]g/m\3\ was revoked,
while the 24-hour standard of 150 [mu]g/m\3\ was retained. On January
15, 2013, EPA promulgated a new NAAQS for PM2.5 (78 FR
3086). The newly promulgated primary annual PM2.5 standard
was set to 12 [mu]g/m\3\, while the remainder of the standards were
retained. The secondary annual PM2.5 standard was retained
at 15 [mu]g/m\3\, the primary and secondary 24-hour standards were
retained at 35 [mu]g/m\3\, the

PM10 primary and secondary 24-hour standards were retained
at 150 [mu]g/m\3\.\1\
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    \1\ See https://www3.epa.gov/ttn/naaqs/standards/pm/s_pm_history.html for a table of the history of the particulate
matter NAAQS. The particulate matter NAAQS can also be found at 40
CFR part 50.
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II. New Mexico's Submittal

    On February 13, 2019, the New Mexico Environment Department (NMED)
submitted a SIP revision for the repeal of 20.2.20 NMAC, certifying
that the State of New Mexico has evaluated its air programs and the New
Mexico SIP and found that the current federal and state regulations are
sufficient to meet CAA requirements after the repeal of 20.2.20 NMAC.
The submittal includes a noninterference demonstration, which contains
information regarding allowable emissions and a modeling demonstration
showing that the repeal will not interfere with attainment or
maintenance of the NAAQS or any other applicable requirement of the
Act. EPA has evaluated NMED's noninterference demonstration and
proposes to conclude that approval of the revision will not interfere
with attainment or maintenance of the NAAQS or any other applicable CAA
requirement. The Technical Support Document (TSD), found in the docket
for this action, provides additional details of certain aspects of the
section 110(l) noninterference demonstration and EPA's evaluation that
are not included in this notice.

A. The Regulation Proposed for Repeal

    The regulation proposed for repeal in New Mexico's February 13,
2019, submittal is Title 20, Chapter 2, Part 20, of the NMAC (20.2.20
NMAC, Lime Manufacturing Plants--Particulate Matter or Part 20), which
covers particulate matter emissions from lime manufacturing plants and
lime hydrators in New Mexico, excluding Albuquerque-Bernalillo County.
Part 20 of 20.2 NMAC was first adopted by the New Mexico Environmental
Improvement Board (EIB) as the Air Quality Control Regulation 509 on
November 15, 1978, and was approved by EPA and adopted into the New
Mexico SIP on April 10, 1980 (45 FR 24460). Since its promulgation,
Part 20 has been reformatted twice, but no substantive changes were
made (62 FR 50514, September 26, 1997).
    Part 20 was adopted to establish control measures to address
potential exceedances of the TSP NAAQS in an area near Hurley, New
Mexico, located in Grant County. That portion of Grant County was
designated as a nonattainment area for TSP, and the State was required
to submit a plan to meet CAA Part D requirements for the attainment and
maintenance of the 1971 TSP NAAQS (43 FR 8962, March 3, 1978). Part 20
incorporated the provisions of 40 CFR part 60, subpart HH, Standards of
Performance for Lime Manufacturing Plants (NSPS Subpart HH),
promulgated by the EPA on March 7, 1978, (43 FR 9452). The TSP NAAQS
and the TSP area designations are no longer in place (61 FR 53639,
October 15, 1996). As discussed in a previous section, the TSP NAAQS
were replaced by the PM10 NAAQS. NSPS Subpart HH was also
revised on April 26, 1984, with the particulate matter emission
standards becoming less stringent (49 FR 18076), but New Mexico did not
revise its SIP to incorporate these changes. The 1984 revision of NSPS
Subpart HH eliminated the performance standards for lime hydrators that
were in the original rule. Part 20 continues to be based on the 1978
version of the NSPS Subpart HH.

B. Particulate Matter Designated Areas in New Mexico

    New Mexico has one particulate matter nonattainment area in
Do[ntilde]a Ana County. The City of Anthony, New Mexico in Do[ntilde]a
Ana County was designated a ``moderate'' nonattainment area for the
1987 PM10 NAAQS (56 FR 56694, November 6, 1991). NMED
determined that all point and area sources of PM10 in or
affecting the area to be de minimis, except for unpaved roads,
unvegetated and sparsely vegetated areas, and range lands. The paving
of roads was determined to be economically infeasible, the enhancement
of ground cover in the region to be technologically infeasible, and
emissions from range lands to be nonanthropogenic (58 FR 18190, April
8, 1993).\2\ This area is still impacted by blowing dust from high
winds, and NMED is developing a dust mitigation plan for both
Do[ntilde]a Ana and Luna counties, as required by EPA's national
Exceptional Events Rule codified at 40 CFR 50.14 (81 FR 68216, October
3, 2016). In addition to the dust mitigation plan, NMED is developing a
fugitive dust rule that will be applicable in areas of the state
requiring a mitigation plan in accordance with 40 CFR 51.930. The rest
of the State of New Mexico is designated attainment/unclassifiable for
PM10, and there are no areas designated nonattainment under
the PM2.5 NAAQS (40 CFR 81.332).
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    \2\ On September 9, 1993, the EPA granted approval of the
Anthony, New Mexico, moderate nonattainment area PM10
SIP, submitted November 8, 1991, including the waiver of the
moderate area attainment date for Anthony, New Mexico (58 FR 47383).
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    As mentioned in the previous section, there was a TSP nonattainment
area based on the 1971 TSP NAAQS within Grant County, which covered a
4.5-mile radius around the Kennecott Copper Smelter, located near the
town of Hurley, New Mexico (44 FR 46895, August 9, 1979). Since then,
the federal TSP standard has been revoked and the smelter has been
closed.

C. Affected Facilities

    There is only one lime facility (Lhoist North America) in New
Mexico, operating with a lime hydrator and no lime kiln, located in the
City of Belen in Valencia County that is subject to Part 20. See Figure
1 in the TSD for a map of New Mexico which portrays the locations of
the Lhoist North America facility and the particulate matter
nonattainment area. The Lhoist North America facility (``Lhoist Belen
Chemical Lime Plant'') in Valencia County is shown to be a long
distance (287 kilometers [km]) away from the only particulate matter
nonattainment area in New Mexico, which is the PM10
nonattainment area in Anthony, Do[ntilde]a Ana County. Lhoist impacts
are negligible on the distant Anthony nonattainment area, and, as a
point of reference, AERMOD \3\ (dispersion model typically used in
PM10 modeling) is only used to model out to 50 km from the
source. Likewise, because of the location of Lhoist in central New
Mexico, Lhoist impacts on air quality in other states are negligible.
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    \3\ AERMOD is the air quality dispersion model developed by
Environmental Protection Agency (EPA), in conjunction with American
Meteorological Society (AMS) to be used as the AMS/EPA Regulatory
Model (AERMOD) promulgated by EPA in 2005 as the preferred
regulatory dispersion model for predicting near-surface pollutant
concentrations within 50 km of an emission source.
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III. The EPA's Evaluation of the State's Submittal and Noninterference
Demonstration

    The repeal of Part 20 eliminates measures for the control of
particulate matter from lime manufacturing plants. While the rule was
instituted to reduce TSP, we must consider the repeal's potential
impact on attainment or maintenance of the current NAAQS for
PM10 and PM2.5. The repeal will only potentially
impact particulate matter emissions. Based upon evaluation of the
permit, no increases in potential to emit of other criteria pollutants
at the Lhoist facility are expected from the repeal of Part 20. The
rule is considered a discretionary measure, as this term was discussed
previously, because TSP

measures included in Part 20 are no longer tied to an area's
classification and no longer mandated by the CAA, and therefore the
control of lime manufacturing is not required to be included in the New
Mexico SIP. Therefore, the rule may be repealed so long as a
demonstration of non-interference is made.
    Section 110(l) prohibits EPA from approving a revision to the SIP
if it would interfere with any applicable requirement concerning
attainment and reasonable further progress (as defined in section 171),
or any other applicable requirement of the Act. The repeal of this rule
will not impact any other applicable requirement. For example, this
measure was not part of New Mexico's SIP to address Regional Haze (77
FR 70693, November 27, 2012; 79 FR 60985, October 9, 2014). In the
following sections, we will address the repeal's potential impact on
CAA requirements, including the attainment of the PM10 and
PM2.5 NAAQS.

A. Potential Impact on Emissions

    While this rule was initially adopted to address multiple
facilities, there is currently only one facility subject to Part 20 in
the State of New Mexico. The one subject facility is owned by Lhoist
North America of Arizona (Lhoist) and is located in the City of Belen,
in Valencia County. Lhoist's Belen Chemical Lime Plant does not operate
a lime kiln and only operates a lime hydrator. The facility receives
quick lime (calcium oxide) and converts it to hydrated lime (calcium
hydroxide) and is an emission source for PM10 and
PM2.5. The Lhoist lime plant has a New Source Review permit
with the State of New Mexico (Permit No. 1652 M2-R7) issued under the
state's SIP-approved permitting program. NSPS Subpart HH and NESHAP
Subpart AAAAA do not cover the Lhoist facility, as the facility does
not operate a lime kiln. Permit provisions for the Lhoist facility,
which include numerical emissions limitations reflected in pounds per
hour (lbs/hr), will remain unchanged if Part 20 is repealed from the
State SIP. These lbs/hr limits are consistent with the limit in Part
20, which is a rate-based limit of 0.15 lbs/ton. NMED provided modeling
based on the allowable emissions in the permit to show that the
particulate matter NAAQS would remain protected. This modeling
demonstration is discussed in a later section.
    The Lhoist facility has a minor New Source Review permit. State
regulations at 20.2.72 NMAC, Construction Permits, (Part 72) have been
incorporated into the New Mexico SIP and was most recently approved on
March 11, 2013 (78 FR 15296). Under the SIP permitting rules,
regardless of the repeal of Part 20, a permit is still required for the
facility, as the particulate matter emissions from the lime hydrator
are estimated to be greater than the 10 lbs/hr or 25 tons/year
permitting thresholds prescribed under Part 72 for minor New Source
Review. Additionally, a permit is required to limit emissions for quick
lime and hydrated lime as those are considered toxic air pollutants
that need to be specifically controlled as required under Part 72
(<IP_ADDRESS>.A.(4), 400, 402, and 502 NMAC). If Lhoist decides to apply
for a permit revision to remove the Part 20 requirements, Lhoist North
America would have to show that their facility would still be able to
comply with the NAAQS as required by their permit and Part 72. Permit
Condition #l(f) of the Lhoist permit states that: ``Changes in plans,
specifications, and other representations stated in the application
documents shall not be made if they cause a change in the method of
control of emissions or in the character of emissions, or will increase
the discharge of emissions. Any such proposed changes shall be
submitted as a revision or modification . . . of this permit.'' NMED
stated in the submittal that should Lhoist apply for a permit revision
in response to the repeal of Part 20 (e.g. to remove Permit Condition
#l(e) which cites to Part 20), Part 72 still requires the applicant to
show compliance with the NAAQS through modeling.
    Please see the State's submittal for this action for the complete
text of the regulation proposed for repeal. Table 1 of the TSD provides
a description and citations of the individual sections of Part 20, as
well as applicable portions of the State and federal regulations for
comparison purposes.
    The New Mexico rules at Part 20 cover both facilities with lime
kilns and those with lime hydrators. Currently, there are no lime
manufacturing facilities that operate lime kilns in New Mexico. New
lime manufacturing facilities in New Mexico subject to the applicable
requirements would be required to apply for a permit with enforceable
emissions limits, pursuant to Part 72. Currently, the only facility
subject to Part 20 is Lhoist North America, which operates a lime
hydrator, but does not operate a lime kiln. Even with the repeal of
Part 20, Lhoist North America will still be subject to Part 72.

B. Air Quality Modeling Demonstration for Lhoist North America

    As part of its noninterference demonstration, NMED submitted a
modeling demonstration showing how the only lime facility in New Mexico
subject to Part 20, Lhoist North America's Belen Chemical Lime Plant,
does not interfere with attainment of the NAAQS at its full potential
to emit. The facility is a baseline source for both PM10 and
PM2.5 prevention of significant deterioration (PSD)
increment.\4\ Therefore, most of the facility emissions do not consume
increment (just emissions above the baseline emission rate), and the
facility has minimal impacts on both Class I and Class II increment
consumption.\5\ We are providing a brief summary of our analysis of New
Mexico's modeling supporting this proposal; please see the TSD for this
notice for our more detailed analysis and review.
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    \4\ PSD increment consumption occurs when emissions increases
occur after the major source baseline date for major sources (PSD
sources) and after the minor source baseline date for minor sources.
The Lhoist facility is a minor source (for PSD purposes) in Air
Quality Control Region 152. Lhoist's facility was in place
(constructed in 1995) and had emissions prior to the minor source
baseline date for PM10 (March 26, 1997) and
PM2.5 (February 11, 2013). Since the Lhoist facility
emissions were in existence prior to the minor source baseline
dates, only increases in Lhoist facility emissions above the
emissions that were emitted at the time of the minor source baseline
date would consume increment.
    \5\ Given the relatively small permitted emission rates and
relatively low maximum modeled values (30-35% of the NAAQS for the
permitted emission rates), small changes over baseline emission
rates would not create increment consumption issues since the
increment for PM10 (30 [mu]g/m\3\) is 20% of the
PM10 NAAQS, the increment for 24-hour PM2.5 (9
[mu]g/m\3\) is 26% of the 24-hour PM2.5 NAAQS and
increment for annual PM2.5 (4 [mu]g/m\3\) is 33% of the
annual PM2.5 NAAQS. As can be seen in Table 1 of this
Federal Register action, Lhoist's maximum impacts from all permitted
emissions are below the increment levels, so any smaller emission
changes from the baseline emissions would be even lower and would
not be near PSD increment levels.
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    The modeling included in the SIP submittal for this action was
performed in 2017. In the modeling, NMED used the most current version
of AERMOD at the time (AERMOD version 16216) and modeled using
meteorological data from 2013. NMED's modeled values are based on
permitted allowable emissions for Lhoist so they represent the highest
possible emissions allowed by their existing permit. Recent actual
emissions are lower. NMED also included surrounding sources within 35
km and used monitoring data to represent background concentrations
which was added to the maximum design value model values. NMED's
modeling indicated that the maximum modeled design values (with
background

concentrations added) were below the NAAQS (see Table 1).
[GRAPHIC] [TIFF OMITTED] TP08JY20.001

    EPA has performed additional modeling as part of the review of the
submitted SIP revision. We utilized the most recent version of AERMOD
(version 19191 issued in 2019). NMED used one year of meteorology for
their modeling analysis and the 2016 AERMOD version (which was the
current AERMOD version when New Mexico performed the modeling in 2017).
EPA performed additional modeling with the 2019 AERMOD (which is the
current version) and five years of meteorological data to confirm
NMED's conclusion that removal of the New Mexico lime regulations in
Part 20 would not interfere with NAAQS and PSD increments. EPA's
Guideline on Air Quality Models (40 CFR part 51, Appendix W) indicates
that, when available, five consecutive years of meteorology should be
utilized when performing AERMOD modeling. Using the same background
monitoring data that NMED used in its submitted modeling demonstration,
EPA's 5-year modeling results (see Table 2) resulted in similar values
to NMED's 1-year modeling results. Specifically, EPA's modeling
indicated that the maximum cumulative concentrations (from Lhoist and
other modeled sources within 35 km) with monitored background
concentrations added for the 24-hour PM10 concentration is
58.9 [mu]g/m\3\ which is 39.3% of the PM10 24-hour NAAQS of
150 [mu]g/m\3\; the maximum cumulative with monitored background added
for PM2.5 24-hour is 23.3 [mu]g/m\3\ which is 66.6% of the
PM2.5 24-hour NAAQS of 35 [mu]g/m\3\; and the maximum
cumulative with monitored background added for PM2.5 Annual
is 10.5 [mu]g/m\3\ which is 87.5% of the Annual PM2.5 NAAQS
of 12 [mu]g/m\3\. EPA's modeling demonstrated that Lhoist
contributions, using linear scaling, would allow for more than a 55%
increase in emissions and still be below the annual and 24-hour
PM2.5 NAAQS and 24-hour PM10 NAAQS. Even with the
potential changes in emissions from the Lhoist facility that could
occur below permitting thresholds, the changes would not be expected to
exceed the 24-hour PM10 and PM2.5 NAAQS (annual
and 24-hour). In addition, small changes in emissions would also
trigger review pursuant to the existing permit limit discussed
previously (Permit Condition #1(f)). Larger emission changes would
require additional permitting including modeling to confirm that the
NAAQS and PSD increments are not exceeded and the change in emissions
would not interfere with NAAQS or PSD increments.

[GRAPHIC] [TIFF OMITTED] TP08JY20.002

    EPA's modeling results, like NMED's modeling results,\6\
demonstrate that: (1) Maximum impact levels near the Lhoist facility
are below the NAAQS, and (2) the higher impacts from the facility are
near the facility and quickly drop off to less than 50% of the maximum
impact levels at a range of 300 meters or less from the facility. New
Mexico modeled Lhoist's emissions with a 4 km square grid centered
around Lhoist to determine the maximum distance from the Lhoist
fenceline that Lhoist has a significant impact to confirm that the
receptor grid captured all the area that Lhoist's emissions had a
significant impact (the area where the Lhoist emissions model to be
above the PSD Significant Impact Level [PSD SIL] and potentially have a
significant impact on the 24-hour PM10, 24-hour
PM2.5, or annual PM2.5 NAAQS). NMED and EPA then
evaluated the modeling of the Lhoist facility and all other particulate
matter sources within 35 km from Lhoist, added background monitoring
values, and compared the results to the NAAQS and PSD increment. No
areas within the modeled area (4 km square grid centered on Lhoist)
were identified in this analysis that were above the PSD increment or
that were near or above the NAAQS, including where Lhoist emissions
contributed significantly to the maximum modeled design values near the
Lhoist facility. Therefore, Lhoist emissions will not interfere with
continued attainment of the NAAQS nor with PSD increment.
---------------------------------------------------------------------------

    \6\ See TSD for EPA's detailed analysis of NMED's modeling and
modeling results.
---------------------------------------------------------------------------

C. Air Monitoring Data for New Mexico

    NMED and EPA have reviewed monitoring data to consider whether the
repeal of the Part 20 rules could cause potential NAAQS attainment
issues based on measured data. New Mexico's Statewide Air Quality
Surveillance Network was approved into the New Mexico SIP by EPA on
August 6, 1981 (46 FR 40005). New Mexico's air quality surveillance
network undergoes recurrent annual review by EPA, as required by 40 CFR
58.10. On July 9, 2019, NMED submitted its 2019 Annual Air Monitoring
Network Plan (AMNP) that included plans for the particulate matter
NAAQS. In our letter to the NMED dated October 31, 2019, we approved
the 2019 New Mexico AMNP with comments, and in our comments, we stated
that the NMED is currently meeting the network design requirements for
ambient air quality monitoring for particulate matter. The NMED
operates a network of six sites with PM10 State or Local Air
Monitoring Stations (SLAMS) monitors, one site with a PM10
Special Purpose Monitor station, and seven sites with a total of nine
PM2.5 SLAMS monitors.
    NMED stated in its submittal that past monitoring data for New
Mexico for years 2010-2015 show that all counties are well below the
PM2.5 NAAQS, and except for Do[ntilde]a Ana County, are
below the NAAQS for PM10 as well. Exceedances measured for
this period for PM10 in Do[ntilde]a Ana, Luna and San Juan
counties were all flagged by NMED in the EPA's Air Quality System as
exceptional events (high winds or wildfire). As stated earlier in the
notice, Anthony, New Mexico in Do[ntilde]a Ana County was designated
nonattainment for the 1987 p.m.10 NAAQS. NMED concluded that
since elevated PM10 levels in Do[ntilde]a Ana County are
nonanthropogenic and not due to lime manufacturing or lime hydrators,
they would be unaffected by the repeal of Part 20. We agree with NMED
that the repeal of Part 20 will not affect ongoing efforts to reduce
PM10 levels in Anthony, New Mexico.
    Since the SIP submission, additional monitoring data is available.
In the following paragraphs, EPA evaluates the most recent monitoring
data for New Mexico.
    Quality-assured and certified particulate matter monitoring data
for years 2016-2018 contained the following design values for
PM2.5 and PM10, shown in Table 3.\7\ Additional

information on the monitors is provided in the TSD.
---------------------------------------------------------------------------

    \7\ See docket for the 2016-2018 monitoring data containing the
design values for New Mexico that has been retrieved from EPA's Air
Quality System and has been quality-assured and certified by the
EPA. The information taken from these reports and in these tables is
intended for informational use only and does not constitute a
regulatory determination by EPA as whether an area has attained a
NAAQS.
    \8\ The level of the 2012 annual NAAQS for PM2.5 is
12.0 [mu]g/m\3\. The design value for the annual PM2.5
NAAQS is the 3-year average annual mean concentration.
    \9\ The level of the 2006 24-hour NAAQS for PM2.5 is
35 [mu]g/m\3\. The design value for the 24-hour PM2.5
NAAQS is the 3-year average 98th percentile concentration.
    \10\ The level of the 1987 24-hour NAAQS for PM10 is
150 [mu]g/m\3\. The NAAQS metric for the PM10 NAAQS is
the 3-year average expected number of exceedances. The standards are
attained when the expected number of days per calendar year with a
24-hour average concentration above 150 [mu]g/m\3\ is equal to or
less than one.

                Table 3--2016-2018 Particulate Matter Design Value Concentrations for New Mexico
----------------------------------------------------------------------------------------------------------------
                                                                                PM10 design value
                                                 PM2.5 design value    PM2.5 design value    (average estimated
               Location (county)                (annual, [mu]g/m\3\)    (24-hour, [mu]g/      exceedances) \10\
                                                         \8\                m\3\) \9\
----------------------------------------------------------------------------------------------------------------
Bernalillo....................................                   7.8                    20                   0.7
Do[ntilde]a Ana...............................                   8.3                    27                   2.1
Lea...........................................                   7.6                    16  ....................
Luna..........................................  ....................  ....................                     1
----------------------------------------------------------------------------------------------------------------

    Monitoring data for PM2.5 show that all of the listed
New Mexico counties with monitors have design values well below the
annual and 24-hour PM2.5 NAAQS for the years 2016-2018.
Monitoring data for PM10 show that Bernalillo County and
Luna County were at or below the annual PM10 NAAQS for the
2018 design values for years 2016-2018. As a result, measured values of
particulate matter indicate that repeal of Part 20 will not interfere
with attainment of the NAAQS.

D. Summary of EPA's Evaluation

    The requirements of 20.2.20 NMAC are a discretionary requirement of
the New Mexico SIP and not required to be included in the SIP. After
evaluating the State's submittal, we propose to find that the removal
of 20.2.20 NMAC from the New Mexico SIP will not interfere with any
applicable requirement concerning attainment and reasonable further
progress, or any other applicable requirement of the CAA. We base our
finding on the following:
     This rule, while originally intended to apply to multiple
sources, now only applies to one source.
     The one source is also governed by a permit issued under
the SIP-approved permitting requirements of Part 72 that requires
compliance with CAA requirements, including the NAAQS.
     Modeling that shows that this one source at its full
potential to emit emissions will not cause an exceedance of the NAAQS
or PSD increment.
     The nearest particulate matter nonattainment area is 287
km away from this source, and its nonattainment issues are primarily
caused by nonanthropogenic sources. Therefore, the one subject source
will not have an impact on that area.
     Likewise, the one source is located centrally in New
Mexico and will therefore have a negligible impact on any surrounding
state's air quality.
     Finally, review of recent monitoring data does not
indicate particulate matter nonattainment problems to which the source
might contribute.
     There are no other applicable requirements, such as the
New Mexico Regional Haze Plan, with which emissions from the source
could interfere.
    If new sources or modification at the existing source occur, these
changes will have to be approved under NMED's SIP-approved permitting
program to ensure that the changes will not interfere with attainment
and maintenance of the NAAQS.

IV. Proposed Action

    We are proposing to approve New Mexico's February 13, 2019, SIP
submittal that provides modifications to State regulations and update
the federally approved New Mexico SIP accordingly. The SIP revision, if
approved by EPA, will remove 20.2.20 NMAC, Lime Manufacturing Plants--
Particulate Matter, from the New Mexico SIP, codified at 40 CFR part
52, subpart GG, 52.1620, and we propose to find that such a revision
will not adversely affect the attainment of applicable CAA
requirements.

V. Incorporation by Reference

    In this document, the EPA is proposing to amend regulatory text
that includes incorporation by reference. As described in the Proposed
Action section above, the EPA is proposing to remove 20.2.20 NMAC from
the New Mexico SIP, which is incorporated by reference in accordance
with the requirements of 1 CFR part 51.

VI. Statutory and Executive Order Reviews

    Under the CAA, the Administrator is required to approve a SIP
submission that complies with the provisions of the Act and applicable
Federal regulations. 42 U.S.C. 7410(k); 40 CFR 52.02(a). Thus, in
reviewing SIP submissions, the EPA's role is to approve state choices,
provided that they meet the criteria of the CAA. Accordingly, this
action merely proposes to approve state law as meeting Federal
requirements and does not impose additional requirements beyond those
imposed by state law. For that reason, this action:
     Is not a ``significant regulatory action'' subject to
review by the Office of Management and Budget under Executive Orders
12866 (58 FR 51735, October 4, 1993) and 13563 (76 FR 3821, January 21,
2011);
     Is not an Executive Order 13771 (82 FR 9339, February 2,
2017) regulatory action because SIP approvals are exempted under
Executive Order 12866;
     Does not impose an information collection burden under the
provisions of the Paperwork Reduction Act (44 U.S.C. 3501 et seq.);
     Is certified as not having a significant economic impact
on a substantial number of small entities under the Regulatory
Flexibility Act (5 U.S.C. 601 et seq.);
     Does not contain any unfunded mandate or significantly or
uniquely affect small governments, as described in the Unfunded
Mandates Reform Act of 1995 (Pub. L. 104-4);
     Does not have federalism implications as specified in
Executive Order 13132 (64 FR 43255, August 10, 1999);
     Is not an economically significant regulatory action based
on health or safety risks subject to Executive Order 13045 (62 FR
19885, April 23, 1997);

     Is not a significant regulatory action subject to
Executive Order 13211 (66 FR 28355, May 22, 2001);
     Is not subject to requirements of section 12(d) of the
National Technology Transfer and Advancement Act of 1995 (15 U.S.C. 272
note) because application of those requirements would be inconsistent
with the CAA; and
     Does not provide EPA with the discretionary authority to
address, as appropriate, disproportionate human health or environmental
effects, using practicable and legally permissible methods, under
Executive Order 12898 (59 FR 7629, February 16, 1994).
    In addition, the SIP is not approved to apply on any Indian
reservation land or in any other area where EPA or an Indian tribe has
demonstrated that a tribe has jurisdiction. In those areas of Indian
country, the proposed rule does not have tribal implications and will
not impose substantial direct costs on tribal governments or preempt
tribal law as specified by Executive Order 13175 (65 FR 67249, November
9, 2000).

List of Subjects in 40 CFR Part 52

    Environmental protection, Air pollution control, Incorporation by
reference, Particulate matter.

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

    Dated: June 29, 2020.
Kenley McQueen,
Regional Administrator, Region 6.
[FR Doc. 2020-14360 Filed 7-7-20; 8:45 am]
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