National Emission Standards for Hazardous Air Pollutants for Chemical Recovery Combustion Sources at Kraft, Soda, Sulfite, and Stand-Alone Semichemical Pulp Mills; Standards of Performance for Kraft Pulp Mill Affected Sources for Which Construction, Reconstruction, or Modification Commenced After May 23, 2013, 70487-70494 [2020-22938]
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TABLE 2—EPA-APPROVED ARIZONA REGULATIONS
State citation
Title/subject
State effective date
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Article 13 (State Implementation Plan Rules For Specific Locations)
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R18–2–B1302 ............
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Limits on SO2 from
July 1, 2018.
the Hayden Smelter.
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[FR Doc. 2020–23031 Filed 11–4–20; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Parts 60 and 63
[EPA–HQ–OAR–2014–0741; FRL–10015–72–
OAR]
RIN 2060–AU53
National Emission Standards for
Hazardous Air Pollutants for Chemical
Recovery Combustion Sources at
Kraft, Soda, Sulfite, and Stand-Alone
Semichemical Pulp Mills; Standards of
Performance for Kraft Pulp Mill
Affected Sources for Which
Construction, Reconstruction, or
Modification Commenced After May 23,
2013
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
The U.S. Environmental
Protection Agency (EPA) is finalizing
amendments to the National Emission
Standards for Hazardous Air Pollutants
(NESHAP) for Chemical Recovery
Combustion Sources at Kraft, Soda,
Sulfite, and Stand-alone Semichemical
Pulp Mills, and the New Source
Performance Standards (NSPS) for Kraft
Pulp Mills constructed, reconstructed,
or modified after May 23, 2013. The
final rule clarifies how to set operating
limits for smelt dissolving tank (SDT)
scrubbers used at these mills and
corrects cross-reference errors in both
rules.
SUMMARY:
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EPA approval date
This final rule is effective on
November 5, 2020.
ADDRESSES: The EPA has established a
docket for this action under Docket ID
No. EPA–HQ–OAR–2014–0741. All
documents in the docket are listed on
the https://www.regulations.gov/
website. Although listed, some
DATES:
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[Insert Federal Register Citation], November 5, 2020.
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ADI Applicability Determination Index
CAA Clean Air Act
CFR Code of Federal Regulations
CRA Congressional Review Act
EPA U.S. Environnemental Protection
Agency
ESP electrostatic precipitator
HAP hazardous air pollutant(s)
NAICS North American Industry
Classification System
NESHAP national emission standards for
hazardous air pollutants
NSPS new source performance standards
NTTAA National Technology Transfer and
Advancement Act
OMB Office of Management and Budget
PFLA percent full load amperage
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Submitted on April 6, 2017. EPA issued a
limited approval and limited disapproval of
Rule R18–2–B1302.
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information is not publicly available,
e.g., Confidential Business Information
or other information whose disclosure is
restricted by statute. Certain other
material, such as copyrighted material,
is not placed on the internet and will be
publicly available only in hard copy
form. Publicly available docket
materials are available electronically
through https://www.regulations.gov/.
Out of an abundance of caution for
members of the public and our staff, the
EPA Docket Center and Reading Room
are closed to the public, with limited
exceptions, to reduce the risk of
transmitting COVID–19. Our Docket
Center staff will continue to provide
remote customer service via email,
phone, and webform.
FOR FURTHER INFORMATION CONTACT: For
questions about this final action, contact
Dr. Kelley Spence, Sector Policies and
Programs Division (E143–03), Office of
Air Quality Planning and Standards,
U.S. Environmental Protection Agency,
Research Triangle Park, North Carolina
27711; telephone number: (919) 541–
3158; fax number: (919) 541–0516; and
email address: spence.kelley@epa.gov.
SUPPLEMENTARY INFORMATION:
Preamble acronyms and
abbreviations. We use multiple
acronyms and terms in this preamble.
While this list may not be exhaustive, to
ease the reading of this preamble and for
reference purposes, the EPA defines the
following terms and acronyms here:
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Additional explanation
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PM particulate matter
PRA Paperwork Reduction Act
RFA Regulatory Flexibility Act
RPM revolutions per minute
SDT smelt dissolving tank
UMRA Unfunded Mandates Reform Act
Background information. On October
31, 2019, the EPA proposed revisions to
the NESHAP for Chemical Recovery
Combustion Sources at Kraft, Soda,
Sulfite, and Stand-Alone Semichemical
Pulp Mills (40 CFR part 63, subpart
MM) and the NSPS for Kraft Pulp Mills
Constructed, Reconstructed, or Modified
After May 23, 2013 (40 CFR part 60,
subpart BBa) clarifying how to set
operating limits for SDT scrubbers used
at these mills and correcting crossreference errors in both rules. The rules
have similar requirements for setting
operating limits for SDT scrubbers,
therefore, similar revisions were
proposed for both rules. See 84 FR
58356. In this action, the EPA is
finalizing the proposed revisions with
minor edits. The preamble includes a
summary of the comments the EPA
received and our responses resulting in
improvements to the proposed rule. A
summary of all public comments on the
proposal and the EPA’s specific
responses to those comments is
provided in the memorandum,
‘‘Response to Comments to Proposed
Rule Amending 40 CFR part 63 Subpart
MM and 40 CFR part 60 Subpart BBa,’’
included in the docket for this action.
Redline versions of the regulatory
language for 40 CFR part 63, subpart
MM, and 40 CFR part 60, subpart BBa
showing the final amendments resulting
from this action and are also available
in the docket.
Organization of this document. The
information in this preamble is
organized as follows:
I. General Information
A. Does this action apply to me?
B. Where can I get a copy of this document
and other related information?
C. Judicial Review and Administrative
Reconsideration
II. Final Amendments
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A. What are the final amendments to the
NESHAP?
B. What are the final amendments to the
NSPS?
III. Summary of Cost, Environmental, and
Economic Impacts
A. What are the affected sources?
B. What are the air quality impacts?
C. What are the cost impacts?
D. What are the economic impacts?
E. What are the benefits?
IV. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory
Planning and Review and Executive
Order 13563: Improving Regulation and
Regulatory Review
B. Executive Order 13771: Reducing
Regulations and Controlling Regulatory
Costs
C. Paperwork Reduction Act (PRA)
D. Regulatory Flexibility Act (RFA)
E. Unfunded Mandates Reform Act
(UMRA)
F. Executive Order 13132: Federalism
G. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
H. Executive Order 13045: Protection of
Children From Environmental Health
Risks and Safety Risks
I. Executive Order 13211: Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use
J. National Technology Transfer and
Advancement Act (NTTAA)
K. Executive Order 12898: Federal Actions
To Address Environmental Justice in
Minority Populations and Low-Income
Populations
L. Congressional Review Act (CRA)
I. General Information
A. Does this action apply to me?
Table 1 of this preamble lists the
NESHAP, NSPS, and associated
regulated industrial source categories
that are the subject of this final rule.
Table 1 is not intended to be exhaustive,
but rather provides a guide for readers
regarding the entities that this final
action is likely to affect. The final
amendments, once promulgated, will be
directly applicable to the affected
sources. Federal, state, local, and tribal
government entities will not be affected
by this action. As defined in the Initial
List of Categories of Sources Under
Section 112(c)(1) of the Clean Air Act
Amendments of 1990 (see 57 FR 31576,
July 16, 1992) and Documentation for
Developing the Initial Source Category
List, Final Report (see EPA–450/3–91–
030, July 1992), the Pulp and Paper
Production source category is any
facility engaged in the production of
pulp and/or paper. This category
includes, but is not limited to,
integrated mills (where pulp alone or
pulp and paper or paperboard are
manufactured on-site), non-integrated
mills (where paper or paperboard are
manufactured, but no pulp is
manufactured on-site), and secondary
fiber mills (where waste paper is used
as the primary raw material). Examples
of pulping methods include kraft, soda,
sulfite, semi-chemical, and mechanical.
The pulp and paper production process
units include operations such as
pulping, bleaching, and chemical
recovery. A kraft pulp mill is defined as
a facility engaged in kraft pulping and
includes digester systems, brown stock
washer systems, multiple-effect
evaporator systems, condensate stripper
systems, recovery furnaces, SDTs, and
lime kilns.
TABLE 1—REGULATIONS AND INDUSTRIAL SOURCE CATEGORIES AFFECTED BY THIS FINAL ACTION
Source category
Name of action
NAICS 1 code
Pulp and Paper Production.
Kraft Pulp Mills .............
Chemical Recovery Combustion Sources at Kraft, Soda, Sulfite, and Stand-Alone
Semichemical Pulp Mills (40 CFR part 63, subpart MM).
Standards of Performance for Kraft Pulp Mill Affected Sources for Which Construction, Reconstruction, or Modification Commenced After May 23, 2013 (40 CFR part 60, subpart BBa).
32211, 32212, 32213
1
North American Industry Classification System.
B. Where can I get a copy of this
document and other related
information?
In addition to being available in the
docket, an electronic copy of this action
is available on the internet. Following
signature by the EPA Administrator, the
EPA will post a copy of the action at
https://www.epa.gov/stationary-sourcesair-pollution/kraft-soda-sulfite-andstand-alone-semichemical-pulp-millsmact-ii and https://www.epa.gov/
stationary-sources-air-pollution/kraftpulp-mills-new-source-performancestandards-nsps-40-cfr-60. Following
publication in the Federal Register, the
EPA will post the Federal Register
version of the final rule at this same
website.
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C. Judicial Review and Administrative
Reconsideration
Under Clean Air Act (CAA) section
307(b)(1), judicial review of this action
is available only by filing a petition for
review in the United States Court of
Appeals for the District of Columbia
Circuit (the court) by January 4, 2021.
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Under CAA section 307(b)(2), the
requirements established by this final
rule may not be challenged separately in
any civil or criminal proceedings
brought by the EPA to enforce the
requirements.
Section 307(d)(7)(B) of the CAA
further provides that only an objection
to a rule or procedure which was raised
with reasonable specificity during the
period for public comment (including
any public hearing) may be raised
during judicial review. This section also
provides a mechanism for the EPA to
reconsider the rule if the person raising
an objection can demonstrate to the
Administrator that it was impracticable
to raise such objection within the period
for public comment or if the grounds for
such objection arose after the period for
public comment (but within the time
specified for judicial review) and if such
objection is of central relevance to the
outcome of the rule. Any person seeking
to make such a demonstration should
submit a Petition for Reconsideration to
the Office of the Administrator, U.S.
Environmental Protection Agency,
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Room 3000, WJC South Building, 1200
Pennsylvania Ave., NW, Washington,
DC 20460, with a copy to both the
person(s) listed in the preceding FOR
FURTHER INFORMATION CONTACT section,
and the Associate General Counsel for
the Air and Radiation Law Office, Office
of General Counsel (Mail Code 2344A),
U.S. Environmental Protection Agency,
1200 Pennsylvania Ave. NW,
Washington, DC 20460.
II. Final Amendments
With this action, the EPA is finalizing
amendments to the NESHAP for
Chemical Recovery Combustion Sources
at Kraft, Soda, Sulfite, and Stand-Alone
Semichemical Pulp Mills (referred to
hereafter as ‘‘the NESHAP’’) and the
NSPS for Kraft Pulp Mills constructed,
reconstructed, or modified after May 23,
2013 (referred to hereafter as ‘‘the
NSPS’’). The amendments (referred to
hereafter as the ‘‘2019 proposed
amendments’’) were proposed on
October 31, 2019 (84 FR 58356) to
clarify how to set operating limits for
SDT scrubbers used at these mills and
correct cross-reference errors in both
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rules. As explained in this section,
clarification was needed to address
parameter monitoring issues that arose
during implementation of the 2017
amendments to the NESHAP (referred to
hereafter as the ‘‘2017 NESHAP
amendments’’) as a result of the
Agency’s residual risk and technology
review. See 82 FR 47328, October 11,
2017.
A. What are the final amendments to
the NESHAP?
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1. Alternative To Monitoring Pressure
Drop for Certain SDT Scrubbers
The 2017 NESHAP amendments
added fan amperage 1 to 40 CFR
63.864(e)(10)(iii) as an alternative to
monitoring pressure drop for SDT
dynamic scrubbers that operate at
ambient pressure and low-energy
entrainment scrubbers where the fan
speed does not vary. Fan amperage was
added as an alternative monitoring
parameter based on the EPA’s review of
alternative monitoring requests for these
types of SDT scrubbers available in the
EPA’s Applicability Determination
Index (ADI) (81 FR 97074, December 30,
2016). In these previously approved
alternative monitoring requests, the EPA
acknowledged that pressure drop is not
the best indicator of particulate matter
(PM)/hazardous air pollutant (HAP)
control device performance when the
SDT scrubber is a low-energy
entrainment scrubber or a dynamic
scrubber that operates near atmospheric
pressure. Low-energy entrainment
scrubbers use the rotation of the fan
blade to shatter the scrubbing liquid
into fine droplets, while at the same
time accelerating the particles into the
airstream. The PM removal efficiency of
these scrubbers is a function of the
number of liquid droplets produced (to
create a large contacting surface area)
and the velocity of the PM imparted by
the fan blade, which in turn, are
functions of the amount of scrubbing
liquid introduced and the tip speed of
the fan blade. Therefore, the most
important parameters to continuously
monitor are the scrubbing liquid flow
rate and the fan rotational speed (as
indicated by the amperage of the fan
motor or revolutions per minute (RPM)).
In addition to adding fan amperage as
a monitoring parameter, the 2017
NESHAP amendments also specified a
method in 40 CFR 63.864(j)(5)(i)(A) for
setting the fan motor amperage
operating limit, requiring that the
minimum fan amperage operating limit
be set as the lowest of the 1-hour
1 Fan amperage refers to the amperage delivered
to the fan motor.
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average fan amperage values associated
with each run demonstrating
compliance with the applicable
emission limit. The intent of
establishing the operating limit as the
lowest 1-hour average fan amperage was
to demonstrate that the scrubber was
operating as intended and removing
HAP accordingly, because fan amperage
values can be correlated with fan speed.
This seemed reasonable during the
development of the 2017 NESHAP
amendments because the fans on these
units are constant speed fans and
changes in the load to the fan motor
(e.g., changes in gas density/pressure or
fan belt issues) result in changes in the
amperage needed to maintain the
constant speed. For example, a scrubber
operating without any scrubbing liquid
or exhaust gas would pull a certain
amount of amperage on the fan motor to
maintain a constant speed. When the
exhaust gas and scrubbing liquid are
added, the fan motor amperage will
increase to maintain that speed. Based
on this concept, the basis for the fan
motor amperage operating limit in the
2017 NESHAP amendments was that a
drop in fan motor amperage below a
certain point showed that the motor
would no longer turn the fan properly
(because, for example, the belt that
connects the motor to the fan was
slipping or broken), which in turn
would mean the scrubber was not
operating as well as it was during the
emissions performance test.
As facilities began to plan their repeat
performance test required by the 2017
NESHAP amendments and determine
the appropriate operating parameters,
they discovered that the method
dictated to set the fan motor amperage
did not accurately represent proper
scrubber performance and submitted
alternative monitoring requests. The
alternative monitoring requests that EPA
received explained that setting the fan
amperage operating limit as outlined in
the 2017 NESHAP amendments at 40
CFR 63.864(j)(5)(i)(A) could result in a
minimum limit that does not correlate
with scrubber emissions-reduction
performance and cannot be achieved at
all times, leading to deviations of the
amperage operating parameter even
when the fan is turning as designed and
the scrubber is operating properly to
achieve the required HAP reduction.
More details on these alternative
monitoring requests were provided in
the memorandum titled, Smelt
Dissolving Tank Scrubber Operating
Parameter Review, in the docket for the
2019 proposed amendments (EPA
Docket Item No. EPA–HQ–OAR–2014–
0741–0277).
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As explained in the preamble to the
2019 proposed amendments, after
reviewing how the SDT scrubbers in
question operate, the EPA agrees that
use of the average fan motor amperage
measured during the performance test to
establish the fan amperage limit as
dictated in 40 CFR 63.864(j)(5)(i)(A) of
the 2017 NESHAP amendments can be
problematic because it does not
necessarily correlate with proper
operation of the scrubber. The EPA’s
intent with adding the fan motor
amperage alternative as part of the 2017
NESHAP amendments was to add
regulatory flexibility while ensuring
proper scrubber operation, not to
arbitrarily set an operating limit that
may not be met, even while the SDT
scrubber is operating properly. The
requirement for determining the fan
motor amperage during the performance
test to set the minimum limit was
included in the 2017 NESHAP
amendments (40 CFR part 63, subpart
MM) which apply to new and existing
sources (see 82 FR 47328, October 11,
2017) and in the NSPS promulgated in
2014 (40 CFR part 60, subpart BBa)
which applies to new sources only (see
79 FR 18952, April 4, 2014). The issue
was not identified in public comments
on either rule but was discovered as
existing sources began to implement the
2017 NESHAP amendments.
Upon further review of the EPA’s
responses to historical alternative
monitoring requests included in the
ADI, recent requests for alternative
monitoring, and other available
information, we recognize that the
requirement to monitor fan amperage
directly and establish a minimum fan
amperage limit based on the average
amperage measured during the
performance test may result in
deviations even when the scrubber is
properly operating. Some facilities were
approved by the EPA to use indicators
of fan operation closely related to fan
amperage (e.g., RPM) and engineering
design considerations when setting the
site-specific fan amperage limit
indicative of proper scrubber operation.
For more details, see the memorandum
titled Smelt Dissolving Tank Scrubber
Operating Parameter Review, in the
docket for the 2019 proposed
amendments (EPA Docket Item No.
EPA–HQ–OAR–2014–0741–0277).
To continue with our original intent
to measure scrubber performance with
an alternative method in these rules, the
EPA proposed this rule to modify the
language at 40 CFR 63.864(e)(10)(iii)
and (j)(5)(i) to clarify how wet scrubber
parameter limits are to be established
and that fan amperage or RPM can be
used to demonstrate compliance for the
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SDT scrubbers in question. Specifically,
the EPA proposed to replace 40 CFR
63.864(j)(5)(i)(A) with a requirement to
set the minimum scrubbing liquid flow
rate operating limit as the lowest of the
1-hour average scrubbing liquid flow
rate values associated with each test run
demonstrating compliance with the
applicable emission limit. This
requirement was inadvertently left out
of the 2017 NESHAP amendments but
was required by other sections of the
rule. Additionally, we proposed to add
a new subsection, 40 CFR
63.864(j)(5)(i)(B), to clarify how wet
scrubber fan amperage operating limits
should be established.
The proposed text in 40 CFR
63.864(j)(5)(i)(B) included the same
requirement that was previously in the
40 CFR 63.864(j)(5)(i) introductory
paragraph, which stated that the
scrubber pressure drop operating limit
must be set as the lowest of the 1-hour
average pressure drop values associated
with each test run demonstrating
compliance with the applicable
emission limit, but also added that for
dynamic or low-energy entrainment
scrubbers, operating limits could be set
using one of three methods specified in
paragraphs 40 CFR 63.864(j)(5)(i)(B)(1)
through (3).
• In 40 CFR 63.864(j)(5)(i)(B)(1), the
EPA proposed to clarify that, for SDT
dynamic wet scrubbers operating at
ambient pressure or for low-energy
entrainment scrubbers where fan speed
does not vary, the minimum fan
amperage operating limit must be set as
the midpoint between the lowest of the
1-hour average fan amperage values
associated with each test run
demonstrating compliance with the
applicable emission limit and the noload amperage value. Additionally, the
proposed regulatory text specified that
the no-load amperage value must be
determined using manufacturers
specifications or by performing a noload test of the fan motor, and that it
must be verified that the scrubber fan is
operating within 5 percent of the design
RPM during the emissions performance
test. A definition of ‘‘no-load fan
amperage’’ was proposed in 40 CFR
63.861.
• In 40 CFR 63.864(j)(5)(i)(B)(2), the
EPA proposed to allow use of percent
full load amperage (PFLA) to
demonstrate compliance and require
that the minimum PFLA to the fan
motor be set as the percent of full load
amperage under no-load, plus 10
percent. Because the no-load value
represents the amperage pulled by the
motor without a fan belt (i.e., the fan is
not engaged), the additional 10 percent
was proposed to ensure that the belt has
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not broken, and the fan is engaged
during operation. This new subsection
also proposed requiring verification that
the scrubber fan is operating within 5
percent of the design RPM during the
emissions performance test.
• In 40 CFR 63.864(j)(5)(i)(B)(3), the
EPA proposed to allow use of RPM to
demonstrate compliance and a
requirement that the minimum RPM be
set at 95 percent of the design RPM. The
EPA also proposed a conforming
amendment in 40 CFR
63.867(c)(3)(iii)(C)(1) to incorporate this
language.
Commenters on the 2019 proposed
amendments supported the proposed
methods for setting minimum operating
limits in 40 CFR 63.864(j)(5)(i)(B)(1) and
(2), except for the requirement to verify
that the scrubber fan is operating within
5 percent of the design RPM during the
emissions performance test.
Commenters strongly opposed the
requirement to verify the design RPM
for reasons detailed in the response-tocomments memorandum, Response to
Comments to Proposed Rule Amending
40 CFR part 63 Subpart MM and 40 CFR
part 60 Subpart BBa, in the docket for
this action. In brief, the commenters
explained that facilities monitoring fan
amperage may not have instrumentation
in place to monitor fan RPM and may
not have the design RPM value
available; that there are safety issues
associated with attempting to obtain a
one-time measurement of RPM; and that
operating within 5 percent of the design
RPM during the emissions performance
test is irrelevant if the performance test
shows compliance with the PM
emission limit and fan amperage (which
is proportional to RPM) is monitored. In
response to these comments, the
requirement to verify that the scrubber
fan is operating within 5 percent of the
design RPM during the emissions
performance test was removed from the
final rule. All other requirements in 40
CFR 63.864(j)(5)(i)(B)(1) and (2) were
finalized as proposed.
One commenter requested that the
EPA modify the proposed definition of
‘‘no load fan amperage’’ by adding the
following language to the end of the
definition, ‘‘or the coupling to a direct
drive fan was disconnected.’’ The
phrase was added as requested for the
final rule.
Regarding the proposed 40 CFR
63.864(j)(5)(i)(B)(2), a commenter
requested clarification on how the
minimum PFLA operating limit should
be calculated for an SDT scrubber fan
and suggested that the EPA present an
example PLFA calculation in the
preamble to the final rule. In response
to this request, we clarified in the final
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rule that the PFLA is calculated by
dividing the no-load amperage value by
the highest of the 1-hour average fan
amperage values associated with each
test run demonstrating compliance with
the applicable emission limit in 40 CFR
63.862 multiplied by 100 and then
adding 10 percent (emphasis added).
We are including the following example
of how to calculate the minimum PFLA.
However, we are not including this
equation in the final rule to avoid the
need to renumber several subsequent
rule equations.
Minimum PFLA = (No-load fan
amperage/highest 1-hour average of
fan amperages) × 100% + 10%
Where:
• The no-load fan amperage
represents the amperage pulled by the
fan motor when the fan is operating
under no-load determined using
manufacturers specifications or by
performing a no-load test of the fan
motor.
• The highest 1-hour average of fan
amperages is the highest of the 1-hour
average fan amperage values associated
with each test run demonstrating
compliance with the applicable
emission limit in 40 CFR 63.862.
For example, assume Facility ‘‘A’’
performs a no-load test of their SDT
scrubber’s fan motor by running the
motor without the fan belt attached. The
measured fan amperage during the noload test is 70 amperage. During a
performance test of the SDT scrubber,
the highest 1-hour average of the fan
amperage values associated with each of
the three test runs demonstrating
compliance with the applicable
emission limit is 179 amperage. Using
these two amperage values, Facility A
would calculate the PFLA alternative
operating parameter limit for their SDT
scrubber fan as follows:
Minimum PFLA = (70/179) × 100% +
10% = 49%
One commenter addressed the
proposed 40 CFR 63.864(j)(5)(i)(B)(3),
which would require the minimum fan
RPM limit to be set as 5 percent lower
than the design RPM. The commenter
stated that the EPA should revise this
requirement to be 5 percent lower than
the lowest 1-hour average RPM
measured during each test run
demonstrating compliance with the
applicable emission limit. The
commenter explained that a facility
could have modified the fan motor such
that it is no longer operating at the
design RPM, or it could have no
documentation of the design RPM, but
it is the performance of the scrubber
during the stack test that matters. In
response to this comment, 40 CFR
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63.864(j)(5)(i)(B)(3) was finalized by
revising it to require that the minimum
RPM be set as 5 percent lower than the
lowest 1-hour average RPM associated
with each test run demonstrating
compliance with the applicable
emission limit, as requested. The EPA
agrees that an operating limit based on
the lowest 1-hour average RPM
measured during each test run (for
facilities that measure RPM) is adequate
to demonstrate ongoing operation of the
SDT scrubber. The 5-percent margin
suggested by the commenter will allow
for variability. The conforming revisions
to 40 CFR 63.867(c)(3)(iii)(C)(1) that
acknowledge RPM as an operating
parameter for SDT dynamic or lowenergy scrubbers were also finalized as
proposed.
2. Other NESHAP Amendments
In addition to clarifying how to set
SDT fan amperage operating limits, the
EPA also proposed to correct the
following cross-reference errors in the
promulgated 40 CFR part 63, subpart
MM NESHAP:
• An incorrect paragraph reference in
the definition of ‘‘modification’’ in 40
CFR 63.861;
• An incorrect paragraph reference in
40 CFR 63.864(e)(10)(iii), referring to 40
CFR 63.864(e)(3)(i) instead of 40 CFR
63.864(e)(10)(i) as intended;
• Omission of reference to wet
scrubber liquid flow rate in 40 CFR
63.864(j)(5) which specifies how to
establish operating limits; and
• Incorrect paragraph references in 40
CFR 63.864(j)(1), (3), and (5) which
cross-referenced requirements that were
proposed (81 FR 97046, December 30,
2016) but not finalized for establishing
site-specific electrostatic precipitator
(ESP) operating limits for secondary
voltage and secondary current (or total
secondary power) for each ESP
collection field. Instead of finalizing
site-specific ESP operating limits, the
EPA finalized a requirement to maintain
proper operation of the ESP’s automatic
voltage control (82 FR 47328, October
11, 2017), but inadvertently kept the
cross-references to the proposed ESP
operating limits in the final rule.
The EPA did not receive any
comments on the first three corrections
noted above and is finalizing these
amendments as proposed.
A comment was received regarding
the EPA’s proposal to eliminate the
reference to 40 CFR 63.864(e)(1) in 40
CFR 63.864(j)(1), (3), and (5) which
pertain to determination of operating
limits. The commenter stated that the
EPA should also eliminate reference to
40 CFR 63.864(e)(2) in these sections
because 40 CFR 63.864(e)(2) references
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40 CFR 63.864(e)(1). The EPA agrees
with the commenter’s suggestion and
eliminated the cross-reference to 40 CFR
63.864(e)(2) in 40 CFR 63.864(j)(1), (3),
and (5) for the final amendments. 40
CFR 63.864(e)(2) specifies parameter
monitoring requirements for kraft or
soda recovery furnaces or lime kilns
using an ESP followed by a wet
scrubber. 40 CFR 63.864(e)(2) refers to
40 CFR 63.864(e)(1) to require facilities
to maintain proper ESP automatic
voltage control and refers to 40 CFR
63.864(e)(10) to require facilities to
monitor wet scrubber parameters. While
40 CFR 63.864(j)(1), (3), and (5) no
longer reference 40 CFR 63.864(e)(1)
and (2), these sections retain the
reference to 40 CFR 63.864(e)(10) with
respect to wet scrubber operating limits.
B. What are the final amendments to the
NSPS?
1. Alternative To Monitoring Pressure
Drop for Certain SDT Scrubbers
The EPA proposed similar
amendments to the fan amperage
requirements in the NSPS as discussed
in section II.A of this preamble for
consistency between the NESHAP and
NSPS that apply to the same scrubbers.
Specifically, NSPS amendments were
proposed for 40 CFR 60.284a(b)(2)(iii),
(c)(3)(i), (c)(4), and (d)(4)(ii) and 40 CFR
60.287a(b)(4)(i) to add RPM language.
As proposed, 40 CFR 60.284a(c)(4)
referred to the procedures for
establishing the SDT fan amperage
operating limit in the NESHAP (40 CFR
63.864(j)(5)(i)(B)). A commenter
requested that 40 CFR 60.284a(c)(4)
specify how scrubber fan amperage
operating limits should be set rather
than referencing 40 CFR
63.864(j)(5)(i)(B) of the NESHAP (as
proposed). The commenter noted that
incorporation of the NESHAP reference
is inappropriate because it requires the
operating parameter limit to be set based
on a performance test that demonstrates
compliance with the applicable
emission limit in 40 CFR 63.862, not 40
CFR 60.282a. In response to this
comment, the EPA removed the
reference to 40 CFR 63.864(j)(5)(i)(B) in
40 CFR 60.284a(c)(4) and replaced it
with specific language describing how
to set scrubber fan amperage operating
parameter limits. The procedures added
to the NSPS in 40 CFR 60.284a(c)(4) are
consistent with the procedures specified
in the NESHAP. The EPA also added the
definition of ‘‘no-load fan amperage’’ to
40 CFR 60.281a because the definition
is referenced in the language added in
40 CFR 63.864(j)(5)(i)(B).
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70491
2. Other NSPS Amendments
The EPA proposed to correct a crossreference error in the promulgated Kraft
Pulp Mills NSPS (40 CFR part 60,
subpart BBa). Specifically, the EPA
proposed to amend incorrect paragraph
references in 40 CFR 60.285a(b)(1) and
60.285a(d)(1) intended to crossreference the rule’s oxygen correction
equation. No comments were received
on these changes so the EPA is
finalizing these amendments as
proposed.
III. Summary of Cost, Environmental,
and Economic Impacts
A. What are the affected sources?
The sources affected by this action are
chemical pulp mills that use SDTs
equipped with low-energy entrainment
scrubbers or dynamic scrubbers that
operate near atmospheric pressure. We
estimate that there are 54 facilities that
utilize these types of scrubbers.
B. What are the air quality impacts?
There are no air quality impacts
associated with the final amendments.
C. What are the cost impacts?
No cost impacts are estimated to be
associated with this action because the
action serves only to provide regulatory
clarity. This action reduces the
likelihood that facilities will choose to
submit site-specific alternative
monitoring requests but does not change
the scope of any regulatory
requirements.
D. What are the economic impacts?
There are no economic impacts
associated with the final amendments.
E. What are the benefits?
Because these final amendments are
not considered economically significant,
as defined by Executive Order 12866,
and because we did not estimate any
emission reductions associated with the
action, we did not estimate any benefits
from reducing emissions.
IV. Statutory and Executive Order
Reviews
Additional information about these
statutes and Executive Orders can be
found at https://www.epa.gov/lawsregulations/laws-and-executive-orders.
A. Executive Order 12866: Regulatory
Planning and Review and Executive
Order 13563: Improving Regulations
and Regulatory Review
This action is not a significant
regulatory action and was, therefore, not
submitted to the Office of Management
and Budget (OMB) for review.
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B. Executive Order 13771: Reducing
Regulations and Controlling Regulatory
Costs
This action is not an Executive Order
13771 regulatory action because this
action is not significant under Executive
Order 12866.
C. Paperwork Reduction Act (PRA)
This action does not impose any new
information collection burden under the
PRA. OMB has previously approved the
information collection activities
contained in the existing regulation (40
CFR part 63, subpart MM) and has
assigned OMB control number 2060–
0377. This action does not change the
information collection requirements.
D. Regulatory Flexibility Act (RFA)
I certify that this action will not have
a significant economic impact on a
substantial number of small entities
under the RFA. This action will not
impose any requirements on small
entities. This action does not create any
new requirements or burdens, and no
costs are associated with this final
action.
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E. Unfunded Mandates Reform Act
(UMRA)
This action does not contain any
unfunded mandate as described in
UMRA, 2 U.S.C. 1531–1538, and does
not significantly or uniquely affect small
governments. The action imposes no
enforceable duty on any state, local, or
tribal governments or the private sector.
reason to believe may
disproportionately affect children, per
the definition of ‘‘covered regulatory
action’’ in section 2–202 of the
Executive Order. This action is not
subject to Executive Order 13045
because it does not concern an
environmental health risk or safety risk.
I. Executive Order 13211: Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use
This action is not subject to Executive
Order 13211 because it is not a
significant regulatory action under
Executive Order 12866.
J. National Technology Transfer and
Advancement Act (NTTAA)
This rulemaking does not involve
technical standards.
K. Executive Order 12898: Federal
Actions To Address Environmental
Justice in Minority Populations and
Low-Income Populations
The EPA believes that this action does
not have disproportionately high and
adverse human health or environmental
effects on minority populations, lowincome populations, and/or indigenous
peoples, as specified in Executive Order
12898 (59 FR 7629, February 16, 1994).
This action does not affect the level of
protection provided to human health or
the environment.
L. Congressional Review Act (CRA)
F. Executive Order 13132: Federalism
This action does not have federalism
implications. It will not have substantial
direct effects on the states, on the
relationship between the national
government and the states, or on the
distribution of power and
responsibilities among the various
levels of government.
This action is subject to the CRA, and
the EPA will submit a rule report to
each House of the Congress and to the
Comptroller General of the United
States. This action is not a ‘‘major rule’’
as defined by U.S.C. 804(2).
G. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
This action does not have tribal
implications, as specified in Executive
Order 13175. The EPA does not know of
any pulp mills owned or operated by
Indian tribal governments or located
within tribal lands. Thus, Executive
Order 13175 does not apply to this
action.
Environmental protection,
Administrative practice and procedures,
Air pollution control, Intergovernmental
relations, Monitoring requirements.
H. Executive Order 13045: Protection of
Children From Environmental Health
Risks and Safety Risks
The EPA interprets Executive Order
13045 as applying to those regulatory
actions that concern environmental
health or safety risks that the EPA has
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List of Subjects
40 CFR Part 60
40 CFR Part 63
Environmental protection,
Administrative practice and procedures,
Air pollution control, Hazardous
substances, Intergovernmental relations,
Reporting and recordkeeping
requirements.
Andrew Wheeler,
Administrator.
For the reasons set forth in the
preamble, the Environmental Protection
Agency amends 40 CFR parts 60 and 63
as follows:
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PART 60—STANDARDS OF
PERFORMANCE FOR NEW
STATIONARY SOURCES
1. The authority citation for part 60
continues to read as follows:
■
Authority: 42 U.S.C. 7401 et seq.
Subpart BBa—Standards of
Performance for Kraft Pulp Mill
Affected Sources for Which
Construction, Reconstruction, or
Modification Commenced After May 23,
2013
2. In § 60.281a, add in alphabetical
order the definition for ‘‘No-load fan
amperage’’ to read as follows:
■
§ 60.281a
Definitions.
*
*
*
*
*
No-load fan amperage means, for the
purposes of this subpart, the amperage
pulled by the fan motor when the fan is
operating under no-load, specifically the
amperage value the motor would use if
the fan belt was removed or the
coupling to a direct drive fan was
disconnected.
*
*
*
*
*
■ 3. In § 60.284a, revise paragraphs
(b)(2)(iii), (c)(3)(i), (c)(4), and (d)(4)(ii) to
read as follows:
§ 60.284a Monitoring of emissions and
operations.
*
*
*
*
*
(b) * * *
(2) * * *
(iii) As an alternative to pressure drop
measurement under paragraph (b)(2)(i)
of this section, a monitoring device for
measurement of fan amperage or
revolutions per minute (RPM) may be
used for smelt dissolving tank dynamic
scrubbers that operate at ambient
pressure or for low-energy entrainment
scrubbers where the fan speed does not
vary.
*
*
*
*
*
(c) * * *
(3) * * *
(i) Calculate 12-hour block averages
from the recorded measurements of wet
scrubber pressure drop (or smelt
dissolving tank scrubber fan amperage
or RPM) and liquid flow rate (or liquid
supply pressure), as applicable.
*
*
*
*
*
(4) During the initial performance test
required in § 60.285a, the owner or
operator must establish site-specific
operating limits for the monitoring
parameters in paragraphs (b)(2) through
(4) of this section by continuously
monitoring the parameters and
determining the arithmetic average
value of each parameter during the
performance test. The arithmetic
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average of the measured values for the
three test runs establishes your
minimum site-specific operating limit
for each wet scrubber or ESP parameter
(except for smelt dissolving tank
scrubber fan amperage or RPM). For
smelt dissolving tank scrubber fan
amperage, set the minimum operating
limit using one of the methods in
paragraphs (c)(4)(i) or (ii) of this section.
For smelt dissolving tank scrubber RPM,
the minimum RPM must be set as
specified in paragraph (c)(4)(iii) of this
section. Multiple performance tests may
be conducted to establish a range of
parameter values. The owner or operator
may establish replacement operating
limits for the monitoring parameters
during subsequent performance tests
using the test methods in § 60.285a.
(i) The minimum fan amperage
operating limit must be set as the
midpoint between the lowest of the 1hour average fan amperage values
associated with each test run
demonstrating compliance with the
applicable emission limit in § 60.282a
and the no-load amperage value. The
no-load amperage value must be
determined using manufacturers
specifications, or by performing a noload test of the fan motor for each smelt
dissolving tank scrubber; or
(ii) The minimum percent full load
amperage (PFLA) to the fan motor must
be set as the percent of full load
amperage under no-load, plus 10
percent. The PFLA is calculated by
dividing the no-load amperage value by
the highest of the 1-hour average fan
amperage values associated with each
test run demonstrating compliance with
the applicable emission limit in
§ 60.282a multiplied by 100 and then
adding 10 percent. The no-load
amperage value must be determined
using manufacturers specifications, or
by performing a no-load test of the fan
motor for each smelt dissolving tank
scrubber.
(iii) The minimum RPM must be set
as 5 percent lower than the lowest 1hour average RPM associated with each
test run demonstrating compliance with
the applicable emission limit.
*
*
*
*
*
(d) * * *
(4) * * *
(ii) All 12-hour block average scrubber
pressure drop (or fan amperage or RPM,
if used as an alternative under
paragraph (b)(2)(iii) of this section)
measurements below the minimum sitespecific limit established during
performance testing during times when
BLS or lime mud is fired (as applicable),
except during startup and shutdown.
*
*
*
*
*
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4. In § 60.285a, revise paragraphs
(b)(1) and (d)(1) to read as follows:
■
§ 60.285a
Test methods and procedures.
*
*
*
*
*
(b) * * *
(1) Method 5 of appendix A–3 of this
part must be used to determine the
filterable particulate matter
concentration. The sampling time and
sample volume for each run must be at
least 60 minutes and 0.90 dscm (31.8
dscf). Water must be used as the
cleanup solvent instead of acetone in
the sample recovery procedure. The
particulate concentration must be
corrected to the appropriate oxygen
concentration according to
§ 60.284a(c)(1)(iii).
*
*
*
*
*
(d) * * *
(1) Method 16 of appendix A–6 of this
part must be used to determine the TRS
concentration. The TRS concentration
must be corrected to the appropriate
oxygen concentration using the
procedure in § 60.284a(c)(1)(iii). The
sampling time must be at least 3 hours,
but no longer than 6 hours.
*
*
*
*
*
■ 5. In § 60.287a, revise paragraph
(b)(4)(i) to read as follows:
§ 60.287a
Recordkeeping.
*
*
*
*
*
(b) * * *
(4) * * *
(i) Records of the pressure drop of the
gas stream through the control
equipment (or smelt dissolving tank
scrubber fan amperage or RPM), and
*
*
*
*
*
PART 63—NATIONAL EMISSION
STANDARDS FOR HAZARDOUS AIR
POLLUTANTS FOR SOURCE
CATEGORIES
6. The authority citation for part 63
continues to read as follows:
■
Authority: 42 U.S.C. 7401 et seq.
Subpart MM—National Emission
Standards for Hazardous Air Pollutants
for Chemical Recovery Combustion
Sources at Kraft, Soda, Sulfite, and
Stand-Alone Semichemical Pulp Mills
7. In § 63.861, revise the definition for
‘‘Modification’’ and add in alphabetical
order the definition for ‘‘No-load fan
amperage’’ to read as follows:
■
§ 63.861
Definitions.
*
*
*
*
*
Modification means, for the purposes
of § 63.862(a)(1)(ii)(D)(1), any physical
change (excluding any routine part
replacement or maintenance) or
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70493
operational change that is made to the
air pollution control device that could
result in an increase in PM emissions.
*
*
*
*
*
No-load fan amperage means, for
purposes of this subpart, the amperage
pulled by the fan motor when the fan is
operating under no-load, specifically the
amperage value the motor would use if
the fan belt was removed or the
coupling to a direct drive fan was
disconnected.
*
*
*
*
*
■ 8. In § 63.864, revise paragraphs
(e)(10)(iii), (j)(1), (3), and (5) to read as
follows:
§ 63.864
Monitoring requirements.
*
*
*
*
*
(e) * * *
(10) * * *
(iii) As an alternative to pressure drop
measurement under paragraph (e)(10)(i)
of this section, a monitoring device for
measurement of fan amperage or fan
revolutions per minute (RPM) may be
used for smelt dissolving tank dynamic
scrubbers that operate at ambient
pressure or for low-energy entrainment
scrubbers where the fan speed does not
vary.
*
*
*
*
*
(j) * * *
(1) During the initial or periodic
performance test required in § 63.865,
the owner or operator of any affected
source or process unit must establish
operating limits for the monitoring
parameters in paragraphs (e)(10)
through (14) of this section, as
appropriate; or
*
*
*
*
*
(3) The owner or operator of an
affected source or process unit may
establish expanded or replacement
operating limits for the monitoring
parameters listed in paragraphs (e)(10)
through (14) of this section and
established in paragraph (j)(1) or (2) of
this section during subsequent
performance tests using the test
methods in § 63.865.
*
*
*
*
*
(5) New, expanded, or replacement
operating limits for the monitoring
parameter values listed in paragraphs
(e)(10) through (14) of this section
should be determined as described in
paragraphs (j)(5)(i) and (ii) of this
section.
(i) The owner or operator of an
affected source or process unit that uses
a wet scrubber must set minimum
operating limits as described in
paragraph (j)(5)(i)(A) and (B) of this
section.
(A) Set the minimum scrubbing liquid
flow rate operating limit as the lowest
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of the 1-hour average scrubbing liquid
flow rate values associated with each
test run demonstrating compliance with
the applicable emission limit in
§ 63.862.
(B) Set the minimum scrubber
pressure drop operating limit as the
lowest of the 1-hour average pressure
drop values associated with each test
run demonstrating compliance with the
applicable emission limit in § 63.862; or
for a smelt dissolving tank dynamic wet
scrubber operating at ambient pressure
or for low-energy entrainment scrubbers
where fan speed does not vary, set the
minimum operating limit using one of
the methods in paragraph (j)(5)(i)(B)(1)
through (3) of this section.
(1) The minimum fan amperage
operating limit must be set as the
midpoint between the lowest of the 1hour average fan amperage values
associated with each test run
demonstrating compliance with the
applicable emission limit in § 63.862
and the no-load amperage value. The
no-load amperage value must be
determined using manufacturers
specifications, or by performing a noload test of the fan motor for each smelt
dissolving tank scrubber; or
(2) The minimum percent full load
amperage (PFLA) to the fan motor must
be set as the percent of full load
amperage under no-load, plus 10
percent. The PFLA is calculated by
dividing the no-load amperage value by
the highest of the 1-hour average fan
amperage values associated with each
test run demonstrating compliance with
the applicable emission limit in § 63.862
multiplied by 100 and then adding 10
percent. The no-load amperage value
must be determined using
manufacturers specifications, or by
performing a no-load test of the fan
motor for each smelt dissolving tank
scrubber; or
(3) The minimum RPM must be set as
5 percent lower than the lowest 1-hour
average RPM associated with each test
run demonstrating compliance with the
applicable emission limit.
(ii) [Reserved]
*
*
*
*
*
■ 9. In § 63.867, revise paragraph
(c)(3)(iii)(C)(1) to read as follows:
§ 63.867
Reporting requirements.
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*
*
*
*
*
(c) * * *
(3) * * *
(iii) * * *
(C) * * *
(1) The operating limits established
during the performance test for
scrubbing liquid flow rate and pressure
drop across the scrubber (or
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alternatively, fan amperage or RPM if
used for smelt dissolving tank
scrubbers).
*
*
*
*
*
[FR Doc. 2020–22938 Filed 11–4–20; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 180
[EPA–HQ–OPP–2020–0112; FRL–10015–69]
Thiamine Mononitrate; Exemption
From the Requirement of a Tolerance
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
This regulation establishes an
exemption from the requirement of a
tolerance for residues of thiamine
mononitrate (CAS Reg. No. 532–43–4)
when used as an inert ingredient
(enzyme cofactor) in pesticide products
applied to/on all growing crops preharvest, limited to 0.1% (by weight) in
pesticide formulations. SciReg, Inc on
behalf of Valagro, S.p.A submitted a
petition to EPA under the Federal Food,
Drug, and Cosmetic Act (FFDCA),
requesting an establishment of an
exemption from the requirement of a
tolerance. This regulation eliminates the
need to establish a maximum
permissible level for residues of
thiamine mononitrate when used in
accordance with this exemption.
Vitamin B1 is also known as thiamine
mononitrate. Throughout this document
and for purposes of issuing the
tolerance, EPA is using the name
‘‘thiamine mononitrate’’ to be consistent
with standard agency nomenclature for
the identification of this substance.
DATES: This regulation is effective
November 5, 2020. Objections and
requests for hearings must be received
on or before January 4, 2021 and must
be filed in accordance with the
instructions provided in 40 CFR part
178 (see also Unit I.C. of the
SUPPLEMENTARY INFORMATION).
ADDRESSES: The docket for this action,
identified by docket identification (ID)
number EPA–HQ–OPP–2020–0112, is
available at https://www.regulations.gov
or at the Office of Pesticide Programs
Regulatory Public Docket (OPP Docket)
in the Environmental Protection Agency
Docket Center (EPA/DC), West William
Jefferson Clinton Bldg., Rm. 3334, 1301
Constitution Ave. NW, Washington, DC
20460–0001. The Public Reading Room
is open from 8:30 a.m. to 4:30 p.m.,
Monday through Friday, excluding legal
holidays. The telephone number for the
SUMMARY:
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Public Reading Room is (202) 566–1744,
and the telephone number for the OPP
Docket is (703) 305–5805.
Due to the public health concerns
related to COVID–19, the EPA Docket
Center (EPA/DC) and Reading Room is
closed to visitors with limited
exceptions. The staff continues to
provide remote customer service via
email, phone, and webform. For the
latest status information on EPA/DC
services and docket access, visit https://
www.epa.gov/dockets.
FOR FURTHER INFORMATION CONTACT:
Marietta Echeverria, Registration
Division (7505P), Office of Pesticide
Programs, Environmental Protection
Agency, 1200 Pennsylvania Ave. NW,
Washington, DC 20460–0001; main
telephone number: (703) 305–7090;
email address: RDFRNotices@epa.gov.
SUPPLEMENTARY INFORMATION:
I. General Information
A. Does this action apply to me?
You may be potentially affected by
this action if you are an agricultural
producer, food manufacturer, or
pesticide manufacturer. The following
list of North American Industrial
Classification System (NAICS) codes is
not intended to be exhaustive, but rather
provides a guide to help readers
determine whether this document
applies to them. Potentially affected
entities may include:
• Crop production (NAICS code 111).
• Animal production (NAICS code
112).
• Food manufacturing (NAICS code
311).
• Pesticide manufacturing (NAICS
code 32532).
B. How can I get electronic access to
other related information?
You may access a frequently updated
electronic version of 40 CFR part 180
through the Government Printing
Office’s e-CFR site at https://www.ecfr50/
cgi-bin/text-idx?&c=ecfr&tpl=/
ecfrbrowse/Title40/40tab_02.tpl.
C. How can I file an objection or hearing
request?
Under FFDCA section 408(g), 21
U.S.C. 346a, any person may file an
objection to any aspect of this regulation
and may also request a hearing on those
objections. You must file your objection
or request a hearing on this regulation
in accordance with the instructions
provided in 40 CFR part 178. To ensure
proper receipt by EPA, you must
identify docket ID number EPA–HQ–
OPP–2020–0112 in the subject line on
the first page of your submission. All
objections and requests for a hearing
E:\FR\FM\05NOR1.SGM
05NOR1
Agencies
[Federal Register Volume 85, Number 215 (Thursday, November 5, 2020)]
[Rules and Regulations]
[Pages 70487-70494]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2020-22938]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Parts 60 and 63
[EPA-HQ-OAR-2014-0741; FRL-10015-72-OAR]
RIN 2060-AU53
National Emission Standards for Hazardous Air Pollutants for
Chemical Recovery Combustion Sources at Kraft, Soda, Sulfite, and
Stand-Alone Semichemical Pulp Mills; Standards of Performance for Kraft
Pulp Mill Affected Sources for Which Construction, Reconstruction, or
Modification Commenced After May 23, 2013
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: The U.S. Environmental Protection Agency (EPA) is finalizing
amendments to the National Emission Standards for Hazardous Air
Pollutants (NESHAP) for Chemical Recovery Combustion Sources at Kraft,
Soda, Sulfite, and Stand-alone Semichemical Pulp Mills, and the New
Source Performance Standards (NSPS) for Kraft Pulp Mills constructed,
reconstructed, or modified after May 23, 2013. The final rule clarifies
how to set operating limits for smelt dissolving tank (SDT) scrubbers
used at these mills and corrects cross-reference errors in both rules.
DATES: This final rule is effective on November 5, 2020.
ADDRESSES: The EPA has established a docket for this action under
Docket ID No. EPA-HQ-OAR-2014-0741. All documents in the docket are
listed on the https://www.regulations.gov/ website. Although listed,
some information is not publicly available, e.g., Confidential Business
Information or other information whose disclosure is restricted by
statute. Certain other material, such as copyrighted material, is not
placed on the internet and will be publicly available only in hard copy
form. Publicly available docket materials are available electronically
through https://www.regulations.gov/. Out of an abundance of caution
for members of the public and our staff, the EPA Docket Center and
Reading Room are closed to the public, with limited exceptions, to
reduce the risk of transmitting COVID-19. Our Docket Center staff will
continue to provide remote customer service via email, phone, and
webform.
FOR FURTHER INFORMATION CONTACT: For questions about this final action,
contact Dr. Kelley Spence, Sector Policies and Programs Division (E143-
03), Office of Air Quality Planning and Standards, U.S. Environmental
Protection Agency, Research Triangle Park, North Carolina 27711;
telephone number: (919) 541-3158; fax number: (919) 541-0516; and email
address: [email protected].
SUPPLEMENTARY INFORMATION:
Preamble acronyms and abbreviations. We use multiple acronyms and
terms in this preamble. While this list may not be exhaustive, to ease
the reading of this preamble and for reference purposes, the EPA
defines the following terms and acronyms here:
ADI Applicability Determination Index
CAA Clean Air Act
CFR Code of Federal Regulations
CRA Congressional Review Act
EPA U.S. Environnemental Protection Agency
ESP electrostatic precipitator
HAP hazardous air pollutant(s)
NAICS North American Industry Classification System
NESHAP national emission standards for hazardous air pollutants
NSPS new source performance standards
NTTAA National Technology Transfer and Advancement Act
OMB Office of Management and Budget
PFLA percent full load amperage
PM particulate matter
PRA Paperwork Reduction Act
RFA Regulatory Flexibility Act
RPM revolutions per minute
SDT smelt dissolving tank
UMRA Unfunded Mandates Reform Act
Background information. On October 31, 2019, the EPA proposed
revisions to the NESHAP for Chemical Recovery Combustion Sources at
Kraft, Soda, Sulfite, and Stand-Alone Semichemical Pulp Mills (40 CFR
part 63, subpart MM) and the NSPS for Kraft Pulp Mills Constructed,
Reconstructed, or Modified After May 23, 2013 (40 CFR part 60, subpart
BBa) clarifying how to set operating limits for SDT scrubbers used at
these mills and correcting cross-reference errors in both rules. The
rules have similar requirements for setting operating limits for SDT
scrubbers, therefore, similar revisions were proposed for both rules.
See 84 FR 58356. In this action, the EPA is finalizing the proposed
revisions with minor edits. The preamble includes a summary of the
comments the EPA received and our responses resulting in improvements
to the proposed rule. A summary of all public comments on the proposal
and the EPA's specific responses to those comments is provided in the
memorandum, ``Response to Comments to Proposed Rule Amending 40 CFR
part 63 Subpart MM and 40 CFR part 60 Subpart BBa,'' included in the
docket for this action. Redline versions of the regulatory language for
40 CFR part 63, subpart MM, and 40 CFR part 60, subpart BBa showing the
final amendments resulting from this action and are also available in
the docket.
Organization of this document. The information in this preamble is
organized as follows:
I. General Information
A. Does this action apply to me?
B. Where can I get a copy of this document and other related
information?
C. Judicial Review and Administrative Reconsideration
II. Final Amendments
[[Page 70488]]
A. What are the final amendments to the NESHAP?
B. What are the final amendments to the NSPS?
III. Summary of Cost, Environmental, and Economic Impacts
A. What are the affected sources?
B. What are the air quality impacts?
C. What are the cost impacts?
D. What are the economic impacts?
E. What are the benefits?
IV. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory Planning and Review and
Executive Order 13563: Improving Regulation and Regulatory Review
B. Executive Order 13771: Reducing Regulations and Controlling
Regulatory Costs
C. Paperwork Reduction Act (PRA)
D. Regulatory Flexibility Act (RFA)
E. Unfunded Mandates Reform Act (UMRA)
F. Executive Order 13132: Federalism
G. Executive Order 13175: Consultation and Coordination With
Indian Tribal Governments
H. Executive Order 13045: Protection of Children From
Environmental Health Risks and Safety Risks
I. Executive Order 13211: Actions Concerning Regulations That
Significantly Affect Energy Supply, Distribution, or Use
J. National Technology Transfer and Advancement Act (NTTAA)
K. Executive Order 12898: Federal Actions To Address
Environmental Justice in Minority Populations and Low-Income
Populations
L. Congressional Review Act (CRA)
I. General Information
A. Does this action apply to me?
Table 1 of this preamble lists the NESHAP, NSPS, and associated
regulated industrial source categories that are the subject of this
final rule. Table 1 is not intended to be exhaustive, but rather
provides a guide for readers regarding the entities that this final
action is likely to affect. The final amendments, once promulgated,
will be directly applicable to the affected sources. Federal, state,
local, and tribal government entities will not be affected by this
action. As defined in the Initial List of Categories of Sources Under
Section 112(c)(1) of the Clean Air Act Amendments of 1990 (see 57 FR
31576, July 16, 1992) and Documentation for Developing the Initial
Source Category List, Final Report (see EPA-450/3-91-030, July 1992),
the Pulp and Paper Production source category is any facility engaged
in the production of pulp and/or paper. This category includes, but is
not limited to, integrated mills (where pulp alone or pulp and paper or
paperboard are manufactured on-site), non-integrated mills (where paper
or paperboard are manufactured, but no pulp is manufactured on-site),
and secondary fiber mills (where waste paper is used as the primary raw
material). Examples of pulping methods include kraft, soda, sulfite,
semi-chemical, and mechanical. The pulp and paper production process
units include operations such as pulping, bleaching, and chemical
recovery. A kraft pulp mill is defined as a facility engaged in kraft
pulping and includes digester systems, brown stock washer systems,
multiple-effect evaporator systems, condensate stripper systems,
recovery furnaces, SDTs, and lime kilns.
Table 1--Regulations and Industrial Source Categories Affected by This Final Action
----------------------------------------------------------------------------------------------------------------
Source category Name of action NAICS \1\ code
----------------------------------------------------------------------------------------------------------------
Pulp and Paper Production............... Chemical Recovery Combustion 32211, 32212, 32213
Sources at Kraft, Soda,
Sulfite, and Stand-Alone
Semichemical Pulp Mills (40
CFR part 63, subpart MM).
Kraft Pulp Mills........................ Standards of Performance for 322110
Kraft Pulp Mill Affected
Sources for Which
Construction, Reconstruction,
or Modification Commenced
After May 23, 2013 (40 CFR
part 60, subpart BBa).
----------------------------------------------------------------------------------------------------------------
\1\ North American Industry Classification System.
B. Where can I get a copy of this document and other related
information?
In addition to being available in the docket, an electronic copy of
this action is available on the internet. Following signature by the
EPA Administrator, the EPA will post a copy of the action at https://www.epa.gov/stationary-sources-air-pollution/kraft-soda-sulfite-and-stand-alone-semichemical-pulp-mills-mact-ii and https://www.epa.gov/stationary-sources-air-pollution/kraft-pulp-mills-new-source-performance-standards-nsps-40-cfr-60. Following publication in the
Federal Register, the EPA will post the Federal Register version of the
final rule at this same website.
C. Judicial Review and Administrative Reconsideration
Under Clean Air Act (CAA) section 307(b)(1), judicial review of
this action is available only by filing a petition for review in the
United States Court of Appeals for the District of Columbia Circuit
(the court) by January 4, 2021. Under CAA section 307(b)(2), the
requirements established by this final rule may not be challenged
separately in any civil or criminal proceedings brought by the EPA to
enforce the requirements.
Section 307(d)(7)(B) of the CAA further provides that only an
objection to a rule or procedure which was raised with reasonable
specificity during the period for public comment (including any public
hearing) may be raised during judicial review. This section also
provides a mechanism for the EPA to reconsider the rule if the person
raising an objection can demonstrate to the Administrator that it was
impracticable to raise such objection within the period for public
comment or if the grounds for such objection arose after the period for
public comment (but within the time specified for judicial review) and
if such objection is of central relevance to the outcome of the rule.
Any person seeking to make such a demonstration should submit a
Petition for Reconsideration to the Office of the Administrator, U.S.
Environmental Protection Agency, Room 3000, WJC South Building, 1200
Pennsylvania Ave., NW, Washington, DC 20460, with a copy to both the
person(s) listed in the preceding FOR FURTHER INFORMATION CONTACT
section, and the Associate General Counsel for the Air and Radiation
Law Office, Office of General Counsel (Mail Code 2344A), U.S.
Environmental Protection Agency, 1200 Pennsylvania Ave. NW, Washington,
DC 20460.
II. Final Amendments
With this action, the EPA is finalizing amendments to the NESHAP
for Chemical Recovery Combustion Sources at Kraft, Soda, Sulfite, and
Stand-Alone Semichemical Pulp Mills (referred to hereafter as ``the
NESHAP'') and the NSPS for Kraft Pulp Mills constructed, reconstructed,
or modified after May 23, 2013 (referred to hereafter as ``the NSPS'').
The amendments (referred to hereafter as the ``2019 proposed
amendments'') were proposed on October 31, 2019 (84 FR 58356) to
clarify how to set operating limits for SDT scrubbers used at these
mills and correct cross-reference errors in both
[[Page 70489]]
rules. As explained in this section, clarification was needed to
address parameter monitoring issues that arose during implementation of
the 2017 amendments to the NESHAP (referred to hereafter as the ``2017
NESHAP amendments'') as a result of the Agency's residual risk and
technology review. See 82 FR 47328, October 11, 2017.
A. What are the final amendments to the NESHAP?
1. Alternative To Monitoring Pressure Drop for Certain SDT Scrubbers
The 2017 NESHAP amendments added fan amperage \1\ to 40 CFR
63.864(e)(10)(iii) as an alternative to monitoring pressure drop for
SDT dynamic scrubbers that operate at ambient pressure and low-energy
entrainment scrubbers where the fan speed does not vary. Fan amperage
was added as an alternative monitoring parameter based on the EPA's
review of alternative monitoring requests for these types of SDT
scrubbers available in the EPA's Applicability Determination Index
(ADI) (81 FR 97074, December 30, 2016). In these previously approved
alternative monitoring requests, the EPA acknowledged that pressure
drop is not the best indicator of particulate matter (PM)/hazardous air
pollutant (HAP) control device performance when the SDT scrubber is a
low-energy entrainment scrubber or a dynamic scrubber that operates
near atmospheric pressure. Low-energy entrainment scrubbers use the
rotation of the fan blade to shatter the scrubbing liquid into fine
droplets, while at the same time accelerating the particles into the
airstream. The PM removal efficiency of these scrubbers is a function
of the number of liquid droplets produced (to create a large contacting
surface area) and the velocity of the PM imparted by the fan blade,
which in turn, are functions of the amount of scrubbing liquid
introduced and the tip speed of the fan blade. Therefore, the most
important parameters to continuously monitor are the scrubbing liquid
flow rate and the fan rotational speed (as indicated by the amperage of
the fan motor or revolutions per minute (RPM)).
---------------------------------------------------------------------------
\1\ Fan amperage refers to the amperage delivered to the fan
motor.
---------------------------------------------------------------------------
In addition to adding fan amperage as a monitoring parameter, the
2017 NESHAP amendments also specified a method in 40 CFR
63.864(j)(5)(i)(A) for setting the fan motor amperage operating limit,
requiring that the minimum fan amperage operating limit be set as the
lowest of the 1-hour average fan amperage values associated with each
run demonstrating compliance with the applicable emission limit. The
intent of establishing the operating limit as the lowest 1-hour average
fan amperage was to demonstrate that the scrubber was operating as
intended and removing HAP accordingly, because fan amperage values can
be correlated with fan speed. This seemed reasonable during the
development of the 2017 NESHAP amendments because the fans on these
units are constant speed fans and changes in the load to the fan motor
(e.g., changes in gas density/pressure or fan belt issues) result in
changes in the amperage needed to maintain the constant speed. For
example, a scrubber operating without any scrubbing liquid or exhaust
gas would pull a certain amount of amperage on the fan motor to
maintain a constant speed. When the exhaust gas and scrubbing liquid
are added, the fan motor amperage will increase to maintain that speed.
Based on this concept, the basis for the fan motor amperage operating
limit in the 2017 NESHAP amendments was that a drop in fan motor
amperage below a certain point showed that the motor would no longer
turn the fan properly (because, for example, the belt that connects the
motor to the fan was slipping or broken), which in turn would mean the
scrubber was not operating as well as it was during the emissions
performance test.
As facilities began to plan their repeat performance test required
by the 2017 NESHAP amendments and determine the appropriate operating
parameters, they discovered that the method dictated to set the fan
motor amperage did not accurately represent proper scrubber performance
and submitted alternative monitoring requests. The alternative
monitoring requests that EPA received explained that setting the fan
amperage operating limit as outlined in the 2017 NESHAP amendments at
40 CFR 63.864(j)(5)(i)(A) could result in a minimum limit that does not
correlate with scrubber emissions-reduction performance and cannot be
achieved at all times, leading to deviations of the amperage operating
parameter even when the fan is turning as designed and the scrubber is
operating properly to achieve the required HAP reduction. More details
on these alternative monitoring requests were provided in the
memorandum titled, Smelt Dissolving Tank Scrubber Operating Parameter
Review, in the docket for the 2019 proposed amendments (EPA Docket Item
No. EPA-HQ-OAR-2014-0741-0277).
As explained in the preamble to the 2019 proposed amendments, after
reviewing how the SDT scrubbers in question operate, the EPA agrees
that use of the average fan motor amperage measured during the
performance test to establish the fan amperage limit as dictated in 40
CFR 63.864(j)(5)(i)(A) of the 2017 NESHAP amendments can be problematic
because it does not necessarily correlate with proper operation of the
scrubber. The EPA's intent with adding the fan motor amperage
alternative as part of the 2017 NESHAP amendments was to add regulatory
flexibility while ensuring proper scrubber operation, not to
arbitrarily set an operating limit that may not be met, even while the
SDT scrubber is operating properly. The requirement for determining the
fan motor amperage during the performance test to set the minimum limit
was included in the 2017 NESHAP amendments (40 CFR part 63, subpart MM)
which apply to new and existing sources (see 82 FR 47328, October 11,
2017) and in the NSPS promulgated in 2014 (40 CFR part 60, subpart BBa)
which applies to new sources only (see 79 FR 18952, April 4, 2014). The
issue was not identified in public comments on either rule but was
discovered as existing sources began to implement the 2017 NESHAP
amendments.
Upon further review of the EPA's responses to historical
alternative monitoring requests included in the ADI, recent requests
for alternative monitoring, and other available information, we
recognize that the requirement to monitor fan amperage directly and
establish a minimum fan amperage limit based on the average amperage
measured during the performance test may result in deviations even when
the scrubber is properly operating. Some facilities were approved by
the EPA to use indicators of fan operation closely related to fan
amperage (e.g., RPM) and engineering design considerations when setting
the site-specific fan amperage limit indicative of proper scrubber
operation. For more details, see the memorandum titled Smelt Dissolving
Tank Scrubber Operating Parameter Review, in the docket for the 2019
proposed amendments (EPA Docket Item No. EPA-HQ-OAR-2014-0741-0277).
To continue with our original intent to measure scrubber
performance with an alternative method in these rules, the EPA proposed
this rule to modify the language at 40 CFR 63.864(e)(10)(iii) and
(j)(5)(i) to clarify how wet scrubber parameter limits are to be
established and that fan amperage or RPM can be used to demonstrate
compliance for the
[[Page 70490]]
SDT scrubbers in question. Specifically, the EPA proposed to replace 40
CFR 63.864(j)(5)(i)(A) with a requirement to set the minimum scrubbing
liquid flow rate operating limit as the lowest of the 1-hour average
scrubbing liquid flow rate values associated with each test run
demonstrating compliance with the applicable emission limit. This
requirement was inadvertently left out of the 2017 NESHAP amendments
but was required by other sections of the rule. Additionally, we
proposed to add a new subsection, 40 CFR 63.864(j)(5)(i)(B), to clarify
how wet scrubber fan amperage operating limits should be established.
The proposed text in 40 CFR 63.864(j)(5)(i)(B) included the same
requirement that was previously in the 40 CFR 63.864(j)(5)(i)
introductory paragraph, which stated that the scrubber pressure drop
operating limit must be set as the lowest of the 1-hour average
pressure drop values associated with each test run demonstrating
compliance with the applicable emission limit, but also added that for
dynamic or low-energy entrainment scrubbers, operating limits could be
set using one of three methods specified in paragraphs 40 CFR
63.864(j)(5)(i)(B)(1) through (3).
In 40 CFR 63.864(j)(5)(i)(B)(1), the EPA proposed to
clarify that, for SDT dynamic wet scrubbers operating at ambient
pressure or for low-energy entrainment scrubbers where fan speed does
not vary, the minimum fan amperage operating limit must be set as the
midpoint between the lowest of the 1-hour average fan amperage values
associated with each test run demonstrating compliance with the
applicable emission limit and the no-load amperage value. Additionally,
the proposed regulatory text specified that the no-load amperage value
must be determined using manufacturers specifications or by performing
a no-load test of the fan motor, and that it must be verified that the
scrubber fan is operating within 5 percent of the design RPM during the
emissions performance test. A definition of ``no-load fan amperage''
was proposed in 40 CFR 63.861.
In 40 CFR 63.864(j)(5)(i)(B)(2), the EPA proposed to allow
use of percent full load amperage (PFLA) to demonstrate compliance and
require that the minimum PFLA to the fan motor be set as the percent of
full load amperage under no-load, plus 10 percent. Because the no-load
value represents the amperage pulled by the motor without a fan belt
(i.e., the fan is not engaged), the additional 10 percent was proposed
to ensure that the belt has not broken, and the fan is engaged during
operation. This new subsection also proposed requiring verification
that the scrubber fan is operating within 5 percent of the design RPM
during the emissions performance test.
In 40 CFR 63.864(j)(5)(i)(B)(3), the EPA proposed to allow
use of RPM to demonstrate compliance and a requirement that the minimum
RPM be set at 95 percent of the design RPM. The EPA also proposed a
conforming amendment in 40 CFR 63.867(c)(3)(iii)(C)(1) to incorporate
this language.
Commenters on the 2019 proposed amendments supported the proposed
methods for setting minimum operating limits in 40 CFR
63.864(j)(5)(i)(B)(1) and (2), except for the requirement to verify
that the scrubber fan is operating within 5 percent of the design RPM
during the emissions performance test. Commenters strongly opposed the
requirement to verify the design RPM for reasons detailed in the
response-to-comments memorandum, Response to Comments to Proposed Rule
Amending 40 CFR part 63 Subpart MM and 40 CFR part 60 Subpart BBa, in
the docket for this action. In brief, the commenters explained that
facilities monitoring fan amperage may not have instrumentation in
place to monitor fan RPM and may not have the design RPM value
available; that there are safety issues associated with attempting to
obtain a one-time measurement of RPM; and that operating within 5
percent of the design RPM during the emissions performance test is
irrelevant if the performance test shows compliance with the PM
emission limit and fan amperage (which is proportional to RPM) is
monitored. In response to these comments, the requirement to verify
that the scrubber fan is operating within 5 percent of the design RPM
during the emissions performance test was removed from the final rule.
All other requirements in 40 CFR 63.864(j)(5)(i)(B)(1) and (2) were
finalized as proposed.
One commenter requested that the EPA modify the proposed definition
of ``no load fan amperage'' by adding the following language to the end
of the definition, ``or the coupling to a direct drive fan was
disconnected.'' The phrase was added as requested for the final rule.
Regarding the proposed 40 CFR 63.864(j)(5)(i)(B)(2), a commenter
requested clarification on how the minimum PFLA operating limit should
be calculated for an SDT scrubber fan and suggested that the EPA
present an example PLFA calculation in the preamble to the final rule.
In response to this request, we clarified in the final rule that the
PFLA is calculated by dividing the no-load amperage value by the
highest of the 1-hour average fan amperage values associated with each
test run demonstrating compliance with the applicable emission limit in
40 CFR 63.862 multiplied by 100 and then adding 10 percent (emphasis
added). We are including the following example of how to calculate the
minimum PFLA. However, we are not including this equation in the final
rule to avoid the need to renumber several subsequent rule equations.
Minimum PFLA = (No-load fan amperage/highest 1-hour average of fan
amperages) x 100% + 10%
Where:
The no-load fan amperage represents the amperage pulled by
the fan motor when the fan is operating under no-load determined using
manufacturers specifications or by performing a no-load test of the fan
motor.
The highest 1-hour average of fan amperages is the highest
of the 1-hour average fan amperage values associated with each test run
demonstrating compliance with the applicable emission limit in 40 CFR
63.862.
For example, assume Facility ``A'' performs a no-load test of their
SDT scrubber's fan motor by running the motor without the fan belt
attached. The measured fan amperage during the no-load test is 70
amperage. During a performance test of the SDT scrubber, the highest 1-
hour average of the fan amperage values associated with each of the
three test runs demonstrating compliance with the applicable emission
limit is 179 amperage. Using these two amperage values, Facility A
would calculate the PFLA alternative operating parameter limit for
their SDT scrubber fan as follows:
Minimum PFLA = (70/179) x 100% + 10% = 49%
One commenter addressed the proposed 40 CFR 63.864(j)(5)(i)(B)(3),
which would require the minimum fan RPM limit to be set as 5 percent
lower than the design RPM. The commenter stated that the EPA should
revise this requirement to be 5 percent lower than the lowest 1-hour
average RPM measured during each test run demonstrating compliance with
the applicable emission limit. The commenter explained that a facility
could have modified the fan motor such that it is no longer operating
at the design RPM, or it could have no documentation of the design RPM,
but it is the performance of the scrubber during the stack test that
matters. In response to this comment, 40 CFR
[[Page 70491]]
63.864(j)(5)(i)(B)(3) was finalized by revising it to require that the
minimum RPM be set as 5 percent lower than the lowest 1-hour average
RPM associated with each test run demonstrating compliance with the
applicable emission limit, as requested. The EPA agrees that an
operating limit based on the lowest 1-hour average RPM measured during
each test run (for facilities that measure RPM) is adequate to
demonstrate ongoing operation of the SDT scrubber. The 5-percent margin
suggested by the commenter will allow for variability. The conforming
revisions to 40 CFR 63.867(c)(3)(iii)(C)(1) that acknowledge RPM as an
operating parameter for SDT dynamic or low-energy scrubbers were also
finalized as proposed.
2. Other NESHAP Amendments
In addition to clarifying how to set SDT fan amperage operating
limits, the EPA also proposed to correct the following cross-reference
errors in the promulgated 40 CFR part 63, subpart MM NESHAP:
An incorrect paragraph reference in the definition of
``modification'' in 40 CFR 63.861;
An incorrect paragraph reference in 40 CFR
63.864(e)(10)(iii), referring to 40 CFR 63.864(e)(3)(i) instead of 40
CFR 63.864(e)(10)(i) as intended;
Omission of reference to wet scrubber liquid flow rate in
40 CFR 63.864(j)(5) which specifies how to establish operating limits;
and
Incorrect paragraph references in 40 CFR 63.864(j)(1),
(3), and (5) which cross-referenced requirements that were proposed (81
FR 97046, December 30, 2016) but not finalized for establishing site-
specific electrostatic precipitator (ESP) operating limits for
secondary voltage and secondary current (or total secondary power) for
each ESP collection field. Instead of finalizing site-specific ESP
operating limits, the EPA finalized a requirement to maintain proper
operation of the ESP's automatic voltage control (82 FR 47328, October
11, 2017), but inadvertently kept the cross-references to the proposed
ESP operating limits in the final rule.
The EPA did not receive any comments on the first three corrections
noted above and is finalizing these amendments as proposed.
A comment was received regarding the EPA's proposal to eliminate
the reference to 40 CFR 63.864(e)(1) in 40 CFR 63.864(j)(1), (3), and
(5) which pertain to determination of operating limits. The commenter
stated that the EPA should also eliminate reference to 40 CFR
63.864(e)(2) in these sections because 40 CFR 63.864(e)(2) references
40 CFR 63.864(e)(1). The EPA agrees with the commenter's suggestion and
eliminated the cross-reference to 40 CFR 63.864(e)(2) in 40 CFR
63.864(j)(1), (3), and (5) for the final amendments. 40 CFR
63.864(e)(2) specifies parameter monitoring requirements for kraft or
soda recovery furnaces or lime kilns using an ESP followed by a wet
scrubber. 40 CFR 63.864(e)(2) refers to 40 CFR 63.864(e)(1) to require
facilities to maintain proper ESP automatic voltage control and refers
to 40 CFR 63.864(e)(10) to require facilities to monitor wet scrubber
parameters. While 40 CFR 63.864(j)(1), (3), and (5) no longer reference
40 CFR 63.864(e)(1) and (2), these sections retain the reference to 40
CFR 63.864(e)(10) with respect to wet scrubber operating limits.
B. What are the final amendments to the NSPS?
1. Alternative To Monitoring Pressure Drop for Certain SDT Scrubbers
The EPA proposed similar amendments to the fan amperage
requirements in the NSPS as discussed in section II.A of this preamble
for consistency between the NESHAP and NSPS that apply to the same
scrubbers. Specifically, NSPS amendments were proposed for 40 CFR
60.284a(b)(2)(iii), (c)(3)(i), (c)(4), and (d)(4)(ii) and 40 CFR
60.287a(b)(4)(i) to add RPM language. As proposed, 40 CFR 60.284a(c)(4)
referred to the procedures for establishing the SDT fan amperage
operating limit in the NESHAP (40 CFR 63.864(j)(5)(i)(B)). A commenter
requested that 40 CFR 60.284a(c)(4) specify how scrubber fan amperage
operating limits should be set rather than referencing 40 CFR
63.864(j)(5)(i)(B) of the NESHAP (as proposed). The commenter noted
that incorporation of the NESHAP reference is inappropriate because it
requires the operating parameter limit to be set based on a performance
test that demonstrates compliance with the applicable emission limit in
40 CFR 63.862, not 40 CFR 60.282a. In response to this comment, the EPA
removed the reference to 40 CFR 63.864(j)(5)(i)(B) in 40 CFR
60.284a(c)(4) and replaced it with specific language describing how to
set scrubber fan amperage operating parameter limits. The procedures
added to the NSPS in 40 CFR 60.284a(c)(4) are consistent with the
procedures specified in the NESHAP. The EPA also added the definition
of ``no-load fan amperage'' to 40 CFR 60.281a because the definition is
referenced in the language added in 40 CFR 63.864(j)(5)(i)(B).
2. Other NSPS Amendments
The EPA proposed to correct a cross-reference error in the
promulgated Kraft Pulp Mills NSPS (40 CFR part 60, subpart BBa).
Specifically, the EPA proposed to amend incorrect paragraph references
in 40 CFR 60.285a(b)(1) and 60.285a(d)(1) intended to cross-reference
the rule's oxygen correction equation. No comments were received on
these changes so the EPA is finalizing these amendments as proposed.
III. Summary of Cost, Environmental, and Economic Impacts
A. What are the affected sources?
The sources affected by this action are chemical pulp mills that
use SDTs equipped with low-energy entrainment scrubbers or dynamic
scrubbers that operate near atmospheric pressure. We estimate that
there are 54 facilities that utilize these types of scrubbers.
B. What are the air quality impacts?
There are no air quality impacts associated with the final
amendments.
C. What are the cost impacts?
No cost impacts are estimated to be associated with this action
because the action serves only to provide regulatory clarity. This
action reduces the likelihood that facilities will choose to submit
site-specific alternative monitoring requests but does not change the
scope of any regulatory requirements.
D. What are the economic impacts?
There are no economic impacts associated with the final amendments.
E. What are the benefits?
Because these final amendments are not considered economically
significant, as defined by Executive Order 12866, and because we did
not estimate any emission reductions associated with the action, we did
not estimate any benefits from reducing emissions.
IV. Statutory and Executive Order Reviews
Additional information about these statutes and Executive Orders
can be found at https://www.epa.gov/laws-regulations/laws-and-executive-orders.
A. Executive Order 12866: Regulatory Planning and Review and Executive
Order 13563: Improving Regulations and Regulatory Review
This action is not a significant regulatory action and was,
therefore, not submitted to the Office of Management and Budget (OMB)
for review.
[[Page 70492]]
B. Executive Order 13771: Reducing Regulations and Controlling
Regulatory Costs
This action is not an Executive Order 13771 regulatory action
because this action is not significant under Executive Order 12866.
C. Paperwork Reduction Act (PRA)
This action does not impose any new information collection burden
under the PRA. OMB has previously approved the information collection
activities contained in the existing regulation (40 CFR part 63,
subpart MM) and has assigned OMB control number 2060-0377. This action
does not change the information collection requirements.
D. Regulatory Flexibility Act (RFA)
I certify that this action will not have a significant economic
impact on a substantial number of small entities under the RFA. This
action will not impose any requirements on small entities. This action
does not create any new requirements or burdens, and no costs are
associated with this final action.
E. Unfunded Mandates Reform Act (UMRA)
This action does not contain any unfunded mandate as described in
UMRA, 2 U.S.C. 1531-1538, and does not significantly or uniquely affect
small governments. The action imposes no enforceable duty on any state,
local, or tribal governments or the private sector.
F. Executive Order 13132: Federalism
This action does not have federalism implications. It will not have
substantial direct effects on the states, on the relationship between
the national government and the states, or on the distribution of power
and responsibilities among the various levels of government.
G. Executive Order 13175: Consultation and Coordination With Indian
Tribal Governments
This action does not have tribal implications, as specified in
Executive Order 13175. The EPA does not know of any pulp mills owned or
operated by Indian tribal governments or located within tribal lands.
Thus, Executive Order 13175 does not apply to this action.
H. Executive Order 13045: Protection of Children From Environmental
Health Risks and Safety Risks
The EPA interprets Executive Order 13045 as applying to those
regulatory actions that concern environmental health or safety risks
that the EPA has reason to believe may disproportionately affect
children, per the definition of ``covered regulatory action'' in
section 2-202 of the Executive Order. This action is not subject to
Executive Order 13045 because it does not concern an environmental
health risk or safety risk.
I. Executive Order 13211: Actions Concerning Regulations That
Significantly Affect Energy Supply, Distribution, or Use
This action is not subject to Executive Order 13211 because it is
not a significant regulatory action under Executive Order 12866.
J. National Technology Transfer and Advancement Act (NTTAA)
This rulemaking does not involve technical standards.
K. Executive Order 12898: Federal Actions To Address Environmental
Justice in Minority Populations and Low-Income Populations
The EPA believes that this action does not have disproportionately
high and adverse human health or environmental effects on minority
populations, low-income populations, and/or indigenous peoples, as
specified in Executive Order 12898 (59 FR 7629, February 16, 1994).
This action does not affect the level of protection provided to human
health or the environment.
L. Congressional Review Act (CRA)
This action is subject to the CRA, and the EPA will submit a rule
report to each House of the Congress and to the Comptroller General of
the United States. This action is not a ``major rule'' as defined by
U.S.C. 804(2).
List of Subjects
40 CFR Part 60
Environmental protection, Administrative practice and procedures,
Air pollution control, Intergovernmental relations, Monitoring
requirements.
40 CFR Part 63
Environmental protection, Administrative practice and procedures,
Air pollution control, Hazardous substances, Intergovernmental
relations, Reporting and recordkeeping requirements.
Andrew Wheeler,
Administrator.
For the reasons set forth in the preamble, the Environmental
Protection Agency amends 40 CFR parts 60 and 63 as follows:
PART 60--STANDARDS OF PERFORMANCE FOR NEW STATIONARY SOURCES
0
1. The authority citation for part 60 continues to read as follows:
Authority: 42 U.S.C. 7401 et seq.
Subpart BBa--Standards of Performance for Kraft Pulp Mill Affected
Sources for Which Construction, Reconstruction, or Modification
Commenced After May 23, 2013
0
2. In Sec. 60.281a, add in alphabetical order the definition for ``No-
load fan amperage'' to read as follows:
Sec. 60.281a Definitions.
* * * * *
No-load fan amperage means, for the purposes of this subpart, the
amperage pulled by the fan motor when the fan is operating under no-
load, specifically the amperage value the motor would use if the fan
belt was removed or the coupling to a direct drive fan was
disconnected.
* * * * *
0
3. In Sec. 60.284a, revise paragraphs (b)(2)(iii), (c)(3)(i), (c)(4),
and (d)(4)(ii) to read as follows:
Sec. 60.284a Monitoring of emissions and operations.
* * * * *
(b) * * *
(2) * * *
(iii) As an alternative to pressure drop measurement under
paragraph (b)(2)(i) of this section, a monitoring device for
measurement of fan amperage or revolutions per minute (RPM) may be used
for smelt dissolving tank dynamic scrubbers that operate at ambient
pressure or for low-energy entrainment scrubbers where the fan speed
does not vary.
* * * * *
(c) * * *
(3) * * *
(i) Calculate 12-hour block averages from the recorded measurements
of wet scrubber pressure drop (or smelt dissolving tank scrubber fan
amperage or RPM) and liquid flow rate (or liquid supply pressure), as
applicable.
* * * * *
(4) During the initial performance test required in Sec. 60.285a,
the owner or operator must establish site-specific operating limits for
the monitoring parameters in paragraphs (b)(2) through (4) of this
section by continuously monitoring the parameters and determining the
arithmetic average value of each parameter during the performance test.
The arithmetic
[[Page 70493]]
average of the measured values for the three test runs establishes your
minimum site-specific operating limit for each wet scrubber or ESP
parameter (except for smelt dissolving tank scrubber fan amperage or
RPM). For smelt dissolving tank scrubber fan amperage, set the minimum
operating limit using one of the methods in paragraphs (c)(4)(i) or
(ii) of this section. For smelt dissolving tank scrubber RPM, the
minimum RPM must be set as specified in paragraph (c)(4)(iii) of this
section. Multiple performance tests may be conducted to establish a
range of parameter values. The owner or operator may establish
replacement operating limits for the monitoring parameters during
subsequent performance tests using the test methods in Sec. 60.285a.
(i) The minimum fan amperage operating limit must be set as the
midpoint between the lowest of the 1-hour average fan amperage values
associated with each test run demonstrating compliance with the
applicable emission limit in Sec. 60.282a and the no-load amperage
value. The no-load amperage value must be determined using
manufacturers specifications, or by performing a no-load test of the
fan motor for each smelt dissolving tank scrubber; or
(ii) The minimum percent full load amperage (PFLA) to the fan motor
must be set as the percent of full load amperage under no-load, plus 10
percent. The PFLA is calculated by dividing the no-load amperage value
by the highest of the 1-hour average fan amperage values associated
with each test run demonstrating compliance with the applicable
emission limit in Sec. 60.282a multiplied by 100 and then adding 10
percent. The no-load amperage value must be determined using
manufacturers specifications, or by performing a no-load test of the
fan motor for each smelt dissolving tank scrubber.
(iii) The minimum RPM must be set as 5 percent lower than the
lowest 1-hour average RPM associated with each test run demonstrating
compliance with the applicable emission limit.
* * * * *
(d) * * *
(4) * * *
(ii) All 12-hour block average scrubber pressure drop (or fan
amperage or RPM, if used as an alternative under paragraph (b)(2)(iii)
of this section) measurements below the minimum site-specific limit
established during performance testing during times when BLS or lime
mud is fired (as applicable), except during startup and shutdown.
* * * * *
0
4. In Sec. 60.285a, revise paragraphs (b)(1) and (d)(1) to read as
follows:
Sec. 60.285a Test methods and procedures.
* * * * *
(b) * * *
(1) Method 5 of appendix A-3 of this part must be used to determine
the filterable particulate matter concentration. The sampling time and
sample volume for each run must be at least 60 minutes and 0.90 dscm
(31.8 dscf). Water must be used as the cleanup solvent instead of
acetone in the sample recovery procedure. The particulate concentration
must be corrected to the appropriate oxygen concentration according to
Sec. 60.284a(c)(1)(iii).
* * * * *
(d) * * *
(1) Method 16 of appendix A-6 of this part must be used to
determine the TRS concentration. The TRS concentration must be
corrected to the appropriate oxygen concentration using the procedure
in Sec. 60.284a(c)(1)(iii). The sampling time must be at least 3
hours, but no longer than 6 hours.
* * * * *
0
5. In Sec. 60.287a, revise paragraph (b)(4)(i) to read as follows:
Sec. 60.287a Recordkeeping.
* * * * *
(b) * * *
(4) * * *
(i) Records of the pressure drop of the gas stream through the
control equipment (or smelt dissolving tank scrubber fan amperage or
RPM), and
* * * * *
PART 63--NATIONAL EMISSION STANDARDS FOR HAZARDOUS AIR POLLUTANTS
FOR SOURCE CATEGORIES
0
6. The authority citation for part 63 continues to read as follows:
Authority: 42 U.S.C. 7401 et seq.
Subpart MM--National Emission Standards for Hazardous Air
Pollutants for Chemical Recovery Combustion Sources at Kraft, Soda,
Sulfite, and Stand-Alone Semichemical Pulp Mills
0
7. In Sec. 63.861, revise the definition for ``Modification'' and add
in alphabetical order the definition for ``No-load fan amperage'' to
read as follows:
Sec. 63.861 Definitions.
* * * * *
Modification means, for the purposes of Sec.
63.862(a)(1)(ii)(D)(1), any physical change (excluding any routine part
replacement or maintenance) or operational change that is made to the
air pollution control device that could result in an increase in PM
emissions.
* * * * *
No-load fan amperage means, for purposes of this subpart, the
amperage pulled by the fan motor when the fan is operating under no-
load, specifically the amperage value the motor would use if the fan
belt was removed or the coupling to a direct drive fan was
disconnected.
* * * * *
0
8. In Sec. 63.864, revise paragraphs (e)(10)(iii), (j)(1), (3), and
(5) to read as follows:
Sec. 63.864 Monitoring requirements.
* * * * *
(e) * * *
(10) * * *
(iii) As an alternative to pressure drop measurement under
paragraph (e)(10)(i) of this section, a monitoring device for
measurement of fan amperage or fan revolutions per minute (RPM) may be
used for smelt dissolving tank dynamic scrubbers that operate at
ambient pressure or for low-energy entrainment scrubbers where the fan
speed does not vary.
* * * * *
(j) * * *
(1) During the initial or periodic performance test required in
Sec. 63.865, the owner or operator of any affected source or process
unit must establish operating limits for the monitoring parameters in
paragraphs (e)(10) through (14) of this section, as appropriate; or
* * * * *
(3) The owner or operator of an affected source or process unit may
establish expanded or replacement operating limits for the monitoring
parameters listed in paragraphs (e)(10) through (14) of this section
and established in paragraph (j)(1) or (2) of this section during
subsequent performance tests using the test methods in Sec. 63.865.
* * * * *
(5) New, expanded, or replacement operating limits for the
monitoring parameter values listed in paragraphs (e)(10) through (14)
of this section should be determined as described in paragraphs
(j)(5)(i) and (ii) of this section.
(i) The owner or operator of an affected source or process unit
that uses a wet scrubber must set minimum operating limits as described
in paragraph (j)(5)(i)(A) and (B) of this section.
(A) Set the minimum scrubbing liquid flow rate operating limit as
the lowest
[[Page 70494]]
of the 1-hour average scrubbing liquid flow rate values associated with
each test run demonstrating compliance with the applicable emission
limit in Sec. 63.862.
(B) Set the minimum scrubber pressure drop operating limit as the
lowest of the 1-hour average pressure drop values associated with each
test run demonstrating compliance with the applicable emission limit in
Sec. 63.862; or for a smelt dissolving tank dynamic wet scrubber
operating at ambient pressure or for low-energy entrainment scrubbers
where fan speed does not vary, set the minimum operating limit using
one of the methods in paragraph (j)(5)(i)(B)(1) through (3) of this
section.
(1) The minimum fan amperage operating limit must be set as the
midpoint between the lowest of the 1-hour average fan amperage values
associated with each test run demonstrating compliance with the
applicable emission limit in Sec. 63.862 and the no-load amperage
value. The no-load amperage value must be determined using
manufacturers specifications, or by performing a no-load test of the
fan motor for each smelt dissolving tank scrubber; or
(2) The minimum percent full load amperage (PFLA) to the fan motor
must be set as the percent of full load amperage under no-load, plus 10
percent. The PFLA is calculated by dividing the no-load amperage value
by the highest of the 1-hour average fan amperage values associated
with each test run demonstrating compliance with the applicable
emission limit in Sec. 63.862 multiplied by 100 and then adding 10
percent. The no-load amperage value must be determined using
manufacturers specifications, or by performing a no-load test of the
fan motor for each smelt dissolving tank scrubber; or
(3) The minimum RPM must be set as 5 percent lower than the lowest
1-hour average RPM associated with each test run demonstrating
compliance with the applicable emission limit.
(ii) [Reserved]
* * * * *
0
9. In Sec. 63.867, revise paragraph (c)(3)(iii)(C)(1) to read as
follows:
Sec. 63.867 Reporting requirements.
* * * * *
(c) * * *
(3) * * *
(iii) * * *
(C) * * *
(1) The operating limits established during the performance test
for scrubbing liquid flow rate and pressure drop across the scrubber
(or alternatively, fan amperage or RPM if used for smelt dissolving
tank scrubbers).
* * * * *
[FR Doc. 2020-22938 Filed 11-4-20; 8:45 am]
BILLING CODE 6560-50-P