Use of Advanced and Emerging Technologies for Quantification of Annual Facility Methane Emissions Under the Greenhouse Gas Reporting Program, 70177-70181 [2024-19403]
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Federal Register / Vol. 89, No. 168 / Thursday, August 29, 2024 / Notices
complex scientific and technical issues
that arise in the development and
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Tentative Agenda:
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• Office of Science Overview and
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Signed in Washington, DC, on August 23,
2024.
Jennifer Hartzell,
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[FR Doc. 2024–19389 Filed 8–28–24; 8:45 am]
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Tentative Agenda Topics
Wednesday, September 25, 2024
• Public Comment
• Presentations by DOE
• Board Business/Open Discussion
Thursday, September 26, 2024
• Public Comment
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• Presentations by DOE
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Signed in Washington, DC on August 23,
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Federal Register Liaison Officer, U.S.
Department of Energy.
[FR Doc. 2024–19401 Filed 8–28–24; 8:45 am]
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ENVIRONMENTAL PROTECTION
AGENCY
[EPA–HQ–OAR–2024–0350; FRL 12138–01–
OAR]
Use of Advanced and Emerging
Technologies for Quantification of
Annual Facility Methane Emissions
Under the Greenhouse Gas Reporting
Program
Environmental Protection
Agency (EPA).
ACTION: Notice; request for information
(RFI).
AGENCY:
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Federal Register / Vol. 89, No. 168 / Thursday, August 29, 2024 / Notices
The EPA invites public
comment on the potential for expanded
use of advanced and emerging
technologies for methane emissions
quantification in EPA’s Greenhouse Gas
Reporting Program (GHGRP). These
technologies are an important part of
EPA’s GHGRP, including under the
recently finalized amendments for
Petroleum and Natural Gas Systems.
EPA intends to use the feedback
received in response to this RFI to
consider whether it is appropriate to
undertake further rulemaking
addressing the use of advanced
measurement technologies in the
GHGRP for petroleum and natural gas
systems and municipal solid waste
(MSW) landfills, beyond the current role
provided in existing rules for these
technologies.
SUMMARY:
Comments must be received on
or before October 28, 2024.
DATES:
Submit your comments,
identified by Docket ID No. EPA–HQ–
OAR–2024–0350, to the Federal Portal:
https://www.regulations.gov. Follow
online instructions for submitting
comments. Once submitted, comments
cannot be edited or withdrawn. Do not
submit electronically any information
you consider to be Confidential
Business Information (CBI). EPA may
publish any comment received to its
public docket, submitted, or sent via
email. For additional submission
methods, the full EPA public comment
policy, information about CBI, and
general guidance on making effective
comments, please visit https://
www.epa.gov/dockets/commenting-epadockets.
ADDRESSES:
FOR FURTHER INFORMATION CONTACT:
Vasco Roma, Environmental Protection
Agency, Office of Air and Radiation,
Office of Atmospheric Protection,
Climate Change Division; telephone
number: 202–564–1662; email address:
Roma.Vasco@epa.gov.
SUPPLEMENTARY INFORMATION:
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I. Background
Technologies with the ability to detect
and measure atmospheric methane have
been advancing significantly over the
last few decades. These technologies are
an important part of EPA programs,
including the recently finalized 40 CFR
part 98 Subpart W (Subpart W)
amendments, which allow for the use of
advanced measurement technologies to
help quantify methane emissions from
Petroleum and Natural Gas Systems
sources, such as emissions from other
large release events and flares under the
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GHGRP.1 Similarly, the oil and natural
gas New Source Performance Standards
and Emission Guidelines at 40 CFR part
60 Subparts OOOOb and OOOOc
(‘‘NSPS OOOOb/EG OOOOc’’)
published in March 2024 allow for the
use of advanced measurement
technologies to identify the presence of
Super Emitter Events and for detecting
fugitive emissions.2 In addition, the
rules provide a pathway for
demonstrating that new technologies
meet the performance requirements
established in the NSPS/EG rules. As a
result, regulated entities are able to
leverage advanced measurement
technologies that are already available
to detect methane emissions rapidly
with accuracy, as well as to incorporate
new technologies that are emerging in
this rapidly evolving field.
Following requests for comment in
the notice of the 2023 proposed
rulemaking for Subpart W,3 the EPA
received numerous comments
requesting that the use of advanced
measurement technologies be allowed to
quantify emissions from other sources
beyond other large release events in
Subpart W. In response to these
comments, EPA reviewed remote
sensing and in situ advanced
measurement approaches (including
both intermittent and continuous
monitoring approaches) that utilize
information from satellite, aerial, drone,
vehicle, and stationary platforms to
detect and/or quantify methane
emissions from oil and gas operations
for their potential use in Subpart W
reporting. As a result of this review and
in response to comments on the
proposed Subpart W rule, in May 2024,
EPA finalized additional options within
Subpart W to use advanced
measurement technologies to measure
data that are inputs to emission
calculations for flares and well
completions and workovers, in addition
to the proposed use of advanced
measurement technologies to quantify
emissions from other large release
events and/or estimate the duration of
such events.
As EPA acknowledged in the final
Subpart W rule, advanced measurement
technologies are developing rapidly and
are particularly well-suited for detecting
1 Final Greenhouse Gas Reporting Rule: Revisions
and Confidentiality Determinations for Petroleum
and Natural Gas Systems, 89 FR 42062 (May 2024).
2 Final Standards of Performance for New,
Reconstructed, and Modified Sources and
Emissions Guidelines for Existing Sources: Oil and
Natural Gas Sector Climate Review, 89 FR 16820
(March 2024).
3 Proposed Greenhouse Gas Reporting Rule:
Revisions and Confidentiality Determinations for
Petroleum and Natural Gas Systems, 88 FR 50282
(August 2023).
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and quantifying large and discrete
emissions events, such as other large
release events. Based on EPA’s
assessment of the strengths and
limitations of advanced measurement
technologies at the time of finalizing the
Subpart W rule, however, EPA limited
the use of these technologies in annual
GHG reporting to certain specific roles
identified in the final rule.4
EPA has also sought comment on how
methane monitoring technologies might
enhance emission estimates for other
industrial sectors covered under the
GHGRP, specifically for MSW landfills
under 40 CFR part 98 Subpart HH
(Subpart HH). In a May 2023 notice of
proposed rulemaking, EPA requested
examples of methane data collected
from available monitoring
methodologies and how such data might
be incorporated into quantifying annual
emissions.5 Although the EPA did not
take final action to incorporate
advanced measurement technologies in
the April 2024 final rule for the reasons
described therein,6 including
information in comments received
noting limitations in existing
technologies, EPA has continued to
review ways to incorporate the use of
advanced measurement technologies
into the emissions reporting for MSW
landfills for GHGRP reporting purposes
under Subpart HH.
Based on these reviews, EPA
recognizes that advanced measurement
technologies, and their use for annual
quantification of methane emissions, are
evolving rapidly. EPA is committed to
transparent and continual
improvements to its programs to ensure
reporting is accurate and complete.
There are four key considerations
associated with expanding the use of
advanced measurement technologies to
quantify annual methane emissions 7
under the GHGRP in a robust,
transparent, accurate, standardized, and
verifiable way:
4 Final Greenhouse Gas Reporting Rule: Revisions
and Confidentiality Determinations for Petroleum
and Natural Gas Systems, 89 FR 42062 (May 2024).
5 Proposed Revisions and Confidentiality
Determinations for Data Elements Under the
Greenhouse Gas Reporting Rule, 88 FR 32852 (May
2023).
6 Final Revisions and Confidentiality
Determinations for Data Elements Under the
Greenhouse Gas Reporting Rule, 89 FR 31802 (April
2024).
7 Current GHGRP reporting requires
quantification of methane emissions at the
equipment-, process-, or facility-level. For example,
under Subpart W emissions are quantified and
reported for specific equipment types, such as
pneumatic controllers. For Subpart HH, emissions
are quantified and reported at the facility-scale,
which includes the total surface area of the landfill,
or for specific processes such as landfill gas
collection and control systems.
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(1) How to translate the measurement
data provided by different types of
advanced measurement technologies
(e.g., methane plume images, satellite
retrievals of column methane mixing
ratios, ambient methane concentrations)
into total tons of methane emissions.
(2) How to extrapolate methane
emissions from discrete and intermittent
observations into total methane
emissions throughout the year (with a
specific level of accuracy) and attribute
these emissions to a specific equipment
type, process, or facility.
(3) How to identify, attribute, and
quantify methane emission events that
are below a technology’s detection limit,
in order to estimate total equipment-,
process-, or facility-level emissions
throughout the year.
(4) How to set detection,
quantification, attribution, verification,
and uncertainty criteria and/or
protocols for different types of advanced
measurement technologies to ensure
implementation into the GHGRP in a
manner that is applicable to different
infrastructures and environmental
conditions across the U.S. (e.g.,
topographies, climates, facility types
and layouts).
As technologies continue to rapidly
advance to meet these needs, EPA is
issuing this RFI to the public to obtain
information about currently available
advanced and emerging methane
measurement technologies, and how
these technologies could be used to
quantify annual methane emissions
from the oil and gas and MSW landfill
industry segments at the equipment-,
process-, or facility-level for GHGRP
reporting purposes. The following
questions are aimed to address the key
considerations outlined above and have
been organized into the following
categories: quantification, attribution,
and implementation.
EPA believes that standards or
protocols could help ensure the use of
advanced measurement technologies to
quantify annual methane emissions is
implemented in a transparent and
standardized manner. Furthermore, EPA
anticipates that annual quantification
approaches may be specific to an
emission source, facility type, or type of
technology. Therefore, a potential
standard or protocol might be specific to
a type of methane source (e.g.,
hydrocarbon liquid storage tanks,
landfill working face) and a specific
measurement approach (e.g., drone,
aircraft, vehicle-based, or multi-platform
based). For example, for a specific type
of source, a potential standard or
protocol might include a detection limit
below a certain methane emissions rate
threshold, a sampling frequency and
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duration (e.g., 1 overpass weekly) to
ensure representative sampling of
operating activities throughout the
reporting year, the inclusion of specific
ancillary data (e.g., wind speed and
direction), and the use of a transparent
and peer-reviewed methodology (e.g.,
inverse analysis, statistical sampling) to
quantify the annual total methane
emissions to within a specified level of
accuracy (e.g., 90%). To the extent that
information provided in response to the
questions below are specific to a
particular emissions source, facility
type, or technology type, please indicate
the applicability in the comments
provided.
II. Questions
1. Quantification of Annual Emission
Rates
EPA is requesting information on
issues related to the quantification of
methane emissions using currently
available advanced measurement
technologies, including: (1) detection
and quantification of methane emission
rates; (2) approaches for extrapolating
observation-based methane emission
rates to estimate annual total emissions;
and (3) approaches for quantifying
annual total methane emissions for
sources that emit at rates below
technology minimum detection
thresholds. Detailed questions on each
topic are listed below. Please provide
detailed answers and citations to
relevant resources.
a. Detection and Quantification of
Atmospheric Methane Emission Events
From Advanced Measurement
Technologies
Advanced technologies for methane
detection, such as instruments deployed
on satellite, aircraft, or in the form of
continuous monitors, can be used to
detect methane emissions. These
technologies do not directly quantify
methane emission rates but require
additional analytical tools and methods
to transform the raw sensor
measurements (e.g., change in light
attenuation) into quantified methane
emission rates (e.g., kg/hour) associated
with each observation. Quantification
approaches can include but are not
limited to the inverse analysis of
observed concentrations, the use of
dispersion modeling, co-emitted tracer
releases, or mass balance approaches.
Based on the wide variety of detection
and quantification approaches currently
available, EPA requests comment on the
following:
i. What advanced measurement
technologies are currently available that
can provide quantified methane
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70179
emission rates using transparent, opensource, and standardized
methodologies? What are the specific
quantification approaches that have
been used with these technologies, and
how have these methodologies been
demonstrated and validated? How can
these technologies and quantification
methodologies be used to provide
annual data in a consistent manner for
each future year of GHGRP reporting?
Are there specific detection and
quantification approaches or
methodologies that EPA should or
should not consider?
ii. What performance metrics and
threshold(s) related to quantification
would be appropriate to apply to
advanced measurement technologies for
their incorporation into the GHGRP? For
example, should EPA consider:
thresholds for the methane detection
limit (e.g., minimum emissions leak
rate), thresholds for the probability of
detection (e.g., rate of false positives or
negative detections), specific levels of
accuracy for quantification, specific
measurement frequencies, or other?
What would be a feasible approach for
developing these thresholds and
metrics?
iii. Should quantification approaches
be limited to the use of specific
methodologies (e.g., inverse analysis,
mass balance) or specific approaches for
using ancillary datasets (e.g.,
standardized interpolation of wind field
products)?
iv. Are there ongoing efforts outside of
EPA to develop standards or protocols
for methane emissions detection and
quantification from advanced
measurement technologies that would
address any of the questions raised in
this RFI? If so, please specify which
efforts and which question(s) can/will
be answered and when these standards
or protocols will be publicly available.
b. Extrapolating Quantified Methane
Emission Rates To Calculate Annual
Emissions for GHGRP Reporting
Purposes
Different advanced measurement
technologies provide data at different
sampling frequencies (e.g., continuous
to weekly) and durations (e.g., seconds
to hours). Depending on the type of
technology and emissions source
sampled, different approaches have
been used to extrapolate observationbased methane emission rates to
estimate total annual emissions for a
specific region, facility, or site. These
approaches often require additional
information on the frequency and
duration of the sampled emission
events, information on the population of
sampled emission sources, site-specific
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operational activities, or statistical
analytical approaches. EPA seeks
comment on the following:
i. What advanced measurement
technologies are currently available that
can provide annual total methane
emission estimates for specific regions,
facilities, processes, or equipment-level
sources, that use transparent, opensource, and standardized methods? Are
these technologies applicable across the
entire U.S. and could they provide
annual data in a consistent manner for
each future year of GHGRP reporting?
Are there specific annual extrapolation
approaches or methodologies that EPA
should or should not consider?
ii. What accuracy or uncertainty
metrics would be appropriate for
GHGRP reporting purposes? For
example, what level of accuracy in
reported annual methane emissions
should advanced measurement
technologies be required to meet? What
sources of uncertainty are necessary to
consider? Are there other specific
quality assurance or quality control
markers that should be considered to
ensure that annual estimates represent
the methane emissions from all
operational activities throughout the
reporting year, such as specific
measurement frequencies or duration?
What would be a feasible approach for
developing these thresholds and
metrics?
iii. To what extent should standards
and protocols be specific to the type of
methods and ancillary data used (e.g.,
statistical approaches), and to what
extent should standards and protocols
simultaneously consider the specific
type of emission sources being sampled
(e.g., large unintended vs. small routine
emissions event)?
c. Quantifying Annual Methane
Emissions From Emissions Sources
Below Detection Limits of Advanced
Measurement Technologies
Different advanced measurement
technologies also have different
detection thresholds (e.g., ∼1 kg/hr to
above 100 kg/hr), in part dependent on
the distance of the instrument from the
source (e.g., typically larger detection
limit for instruments on satellites
compared to aircraft), instrument type,
and sampling strategy. In the current
GHGRP, a significant number of sources
emit methane at rates below these
typical detection limits (e.g., a
component leak will typically emit at
rates significantly below 1 kg/hr). To
account for methane emissions from
these additional sources, various
methodologies and statistical
approaches have been developed to
estimate total annual emissions to
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complement the data collected from
advanced technology measurements.
EPA seeks comment on the following:
i. What methodologies are currently
available for integrating estimates of
methane emissions for those sources
emitting below technology detection
thresholds in an open-source,
transparent, and standardized way? Can
these methodologies provide annual
data in a consistent manner for each
future year of GHGRP reporting? Are
there specific approaches or
methodologies that EPA should or
should not consider?
ii. Should these quantification
approaches be limited to the use of
specific methodologies (e.g., Monte
Carlo method) or specific ancillary
datasets (e.g., the use of standardized
infrastructure or operator data)?
2. Attribution
EPA is requesting comment and
information regarding attribution of
quantified methane emissions (from
discrete events or annual totals) to
specific GHGRP facilities, sites, or
sources.
In addition to differences in temporal
resolution, advanced measurement
technologies have spatial resolutions
that can range from kilometers (e.g.,
satellite) to site or individual equipment
scales (e.g., ground-based sensors).
There are different approaches for
attributing observed events to a specific
equipment type, process, or facility
depending on the specific type of
technology used and sampling distance
from the emissions source. These
approaches often require ancillary
information such as infrastructure data,
site operator data, or meteorological
data such as wind speed and direction.
EPA seeks comments on the following:
a. What methodologies are currently
available that can attribute quantified
methane emission events to specific
equipment types (or additionally,
specific regions, facilities, or processes)
using transparent, open-source, and
standardized methods? Are there
specific attribution approaches or
methodologies that EPA should or
should not consider?
b. What accuracy or uncertainty
metrics would be appropriate for
GHGRP reporting purposes? For
example, what level of confidence in the
source attribution would be necessary
for advanced measurement technologies
to meet for GHGRP reporting purposes?
What would be a feasible approach for
developing these thresholds?
c. To what extent would standards
and protocols need to be specific to the
type of methods and ancillary data used
(e.g., infrastructure datasets) or the type
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of emission source sampled (e.g., large
unintended vs small routine emissions
event)?
3. Implementation
EPA is requesting comment and
information on issues related to the
implementation of advanced
measurement technologies into the
GHGRP.
Implementation considerations
include the need for quantifying annual
total methane emissions from oil and
gas and MSW landfill applicable
sources across the U.S. in a transparent
and standardized way, validation and
verification of the reported data, and
additional potential uses of advanced
measurement technologies for the
GHGRP. EPA also requests information
on additional data that could be
reported for the verification of methane
emissions estimates produced using
advanced measurement technologies.
a. Structure of Approaches or Protocols
i. What form would standard
method(s) or protocol(s) need to take to
ensure that advanced measurement
technologies provide annual total,
source-specific, methane emissions in a
transparent and standardized way? For
example,
(1) To what extent should standards
and protocols be specific to the type of
methods used (e.g., satellite, aircraft,
ground-based)? In addition, would
different standards or protocols be
necessary for sampling approaches
using single platform vs. multi-platform
measurements? Could standard methods
be developed to be technology agnostic?
(2) To what extent could standard
method(s) be developed to be source
agnostic? For example, would standards
need to be specific to the type of
equipment, process, or emission source
sampled (e.g., tanks, flares, pneumatic
devices, landfill working face), or could
a set of standard(s) be developed to be
more broadly applicable across different
GHGRP industry segments (e.g., oil and
gas operations and landfills)?
Alternatively, would different standards
be necessary for different types of
methane emission events sampled (e.g.,
large unintended vs small routine
emissions events)?
b. Verification and Validation of Annual
Source-specific Methane Emission
Quantification Methods Using
Advanced Measurement Technologies
for GHGRP Reporting Purposes
i. Are there approaches currently
available that could be used to verify
that advanced measurement
technologies meet specific standards
(e.g., independent blind studies,
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deployment of calibration standards,
other)?
ii. Is it necessary to limit the
applicability of advanced measurement
technologies to environmental and site
conditions that have been previously
validated? For example, if an advanced
measurement technology has been
validated through blind control release
testing during which wind speeds
ranged from 0.5 to 10 m/s, should the
technology be limited to measurements
within this range of wind speeds? What
form of validation could be used to
demonstrate whether a technology is
applicable across environmental
conditions outside of their tested
ranges?
iii. Are there specific types of
operator- or facility-specific information
that would be useful for improving or
validating annual methane emissions
quantification or source attribution from
advanced measurement technologies?
c. Other Considerations Related to the
Use of Advanced Measurement
Technologies for GHGRP Reporting
Purposes
i. What (if any) are the current barriers
or limitations to using advanced
measurement technologies beyond what
is currently allowed under the GHGRP
to quantify annual equipment-level
methane emissions at scale in the U.S.?
ii. What are the cost considerations
for implementing different advanced
measurement technologies to quantify
annual, equipment-, process-, or facilitylevel methane emissions for GHGRP
reporting purposes? If available, costs
should be provided in a manner that can
be scaled up to different
implementation approaches (e.g., cost
per site, cost per area covered).
iii. How are factors such as
measurement and analysis cost,
complexity, or time burden relevant for
determining whether advanced
measurement technologies may be
appropriate for annual GHGRP
application?
iv. Other than methane emissions
detection and quantification, and
establishing the duration of emission
events as permitted under Subpart W for
Other Large Release Events, are there
additional ways in which advanced
measurement technologies could be
used to support quantification and
reporting of equipment-, process-, or
facility-level methane emissions to the
GHGRP (e.g., as a method to identify
changes in operating conditions, to
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supplement specific reported data
elements)?
Sharyn Lie,
Director, Climate Change Division.
70181
Agency, 1200 Pennsylvania Ave. NW,
Washington, DC 20460–0001; telephone
number: 202–566–2343; email address:
douglass.james@epa.gov.
[FR Doc. 2024–19403 Filed 8–28–24; 8:45 am]
SUPPLEMENTARY INFORMATION:
BILLING CODE 6560–50–P
I. General Information
A. Does this action apply to me?
ENVIRONMENTAL PROTECTION
AGENCY
[EPA–HQ–OPP–2011–0374; FRL–12220–01–
OCSPP]
Dimethyl Tetrachloroterephthalate
(DCPA); Notice of Receipt of Requests
to Voluntarily Cancel Pesticide
Registrations
Environmental Protection
Agency (EPA).
ACTION: Notice.
AGENCY:
In accordance with the
Federal Insecticide, Fungicide, and
Rodenticide Act (FIFRA), the
Environmental Protection Agency (EPA
or Agency) is issuing a notice of receipt
of requests by the DCPA registrant to
voluntarily cancel DCPA pesticide
registrations. EPA intends to grant these
requests at the close of the comment
period for this announcement unless the
Agency receives substantive comments
within the comment period that would
merit its further review of the requests,
or unless the registrants withdraw its
requests. If these requests are granted,
any sale, distribution, or use of products
listed in this notice will not be
permitted after the registrations have
been cancelled consistent with the
terms as described in the final order.
DATES: Comments must be received on
or before September 30, 2024.
ADDRESSES: Submit your comments,
identified by docket identification (ID)
number EPA–HQ–OPP–2011–0374,
online at https://www.regulations.gov.
Follow the online instructions for
submitting comments. Do not submit
electronically any information you
consider to be Confidential Business
Information (CBI) or other information
whose disclosure is restricted by statute.
Additional instructions on commenting
and visiting the docket, along with more
information about dockets generally, is
available at https://www.epa.gov/
dockets.
FOR FURTHER INFORMATION CONTACT:
James Douglass, Pesticide Re-Evaluation
Division (7508P), Office of Pesticide
Programs, Environmental Protection
SUMMARY:
PO 00000
Frm 00021
Fmt 4703
Sfmt 4703
This action is directed to the public
in general and may be of interest to a
wide range of stakeholders including
environmental, human health, and
agricultural advocates; the chemical
industry; pesticide users; and members
of the public interested in the sale,
distribution, or use of pesticides.
B. What should I consider as I prepare
my comments for EPA?
1. Submitting CBI. Do not submit this
information to EPA through
regulations.gov or email. Clearly mark
the part or all of the information that
you claim to be CBI. For CBI
information in a disk or CD–ROM that
you mail to EPA, mark the outside of the
disk or CD–ROM as CBI and then
identify electronically within the disk or
CD–ROM the specific information that
is claimed as CBI. In addition to one
complete version of the comment that
includes information claimed as CBI, a
copy of the comment that does not
contain the information claimed as CBI
must be submitted for inclusion in the
public docket. Information so marked
will not be disclosed except in
accordance with procedures set forth in
40 CFR part 2.
2. Tips for preparing your comments.
When preparing and submitting your
comments, see the commenting tips at
https://www.epa.gov/dockets/
commenting-epa-dockets.
II. What action is the Agency taking?
This notice announces receipt by the
Agency of requests from the DCPA
registrant to cancel 3 pesticide products
registered under FIFRA section 3 (7
U.S.C. 136a) or section 24(c) (7 U.S.C.
136v(c)). These registrations are listed in
sequence by registration number (or
company number and 24(c) number) in
Table 1 of this unit.
Unless the Agency determines that
there are substantive comments that
warrant further review of the requests or
the registrants withdraw their requests,
EPA intends to issue an order in the
Federal Register canceling all the
affected registrations.
E:\FR\FM\29AUN1.SGM
29AUN1
Agencies
[Federal Register Volume 89, Number 168 (Thursday, August 29, 2024)]
[Notices]
[Pages 70177-70181]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2024-19403]
=======================================================================
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ENVIRONMENTAL PROTECTION AGENCY
[EPA-HQ-OAR-2024-0350; FRL 12138-01-OAR]
Use of Advanced and Emerging Technologies for Quantification of
Annual Facility Methane Emissions Under the Greenhouse Gas Reporting
Program
AGENCY: Environmental Protection Agency (EPA).
ACTION: Notice; request for information (RFI).
-----------------------------------------------------------------------
[[Page 70178]]
SUMMARY: The EPA invites public comment on the potential for expanded
use of advanced and emerging technologies for methane emissions
quantification in EPA's Greenhouse Gas Reporting Program (GHGRP). These
technologies are an important part of EPA's GHGRP, including under the
recently finalized amendments for Petroleum and Natural Gas Systems.
EPA intends to use the feedback received in response to this RFI to
consider whether it is appropriate to undertake further rulemaking
addressing the use of advanced measurement technologies in the GHGRP
for petroleum and natural gas systems and municipal solid waste (MSW)
landfills, beyond the current role provided in existing rules for these
technologies.
DATES: Comments must be received on or before October 28, 2024.
ADDRESSES: Submit your comments, identified by Docket ID No. EPA-HQ-
OAR-2024-0350, to the Federal Portal: https://www.regulations.gov.
Follow online instructions for submitting comments. Once submitted,
comments cannot be edited or withdrawn. Do not submit electronically
any information you consider to be Confidential Business Information
(CBI). EPA may publish any comment received to its public docket,
submitted, or sent via email. For additional submission methods, the
full EPA public comment policy, information about CBI, and general
guidance on making effective comments, please visit https://www.epa.gov/dockets/commenting-epa-dockets.
FOR FURTHER INFORMATION CONTACT: Vasco Roma, Environmental Protection
Agency, Office of Air and Radiation, Office of Atmospheric Protection,
Climate Change Division; telephone number: 202-564-1662; email address:
[email protected].
SUPPLEMENTARY INFORMATION:
I. Background
Technologies with the ability to detect and measure atmospheric
methane have been advancing significantly over the last few decades.
These technologies are an important part of EPA programs, including the
recently finalized 40 CFR part 98 Subpart W (Subpart W) amendments,
which allow for the use of advanced measurement technologies to help
quantify methane emissions from Petroleum and Natural Gas Systems
sources, such as emissions from other large release events and flares
under the GHGRP.\1\ Similarly, the oil and natural gas New Source
Performance Standards and Emission Guidelines at 40 CFR part 60
Subparts OOOOb and OOOOc (``NSPS OOOOb/EG OOOOc'') published in March
2024 allow for the use of advanced measurement technologies to identify
the presence of Super Emitter Events and for detecting fugitive
emissions.\2\ In addition, the rules provide a pathway for
demonstrating that new technologies meet the performance requirements
established in the NSPS/EG rules. As a result, regulated entities are
able to leverage advanced measurement technologies that are already
available to detect methane emissions rapidly with accuracy, as well as
to incorporate new technologies that are emerging in this rapidly
evolving field.
---------------------------------------------------------------------------
\1\ Final Greenhouse Gas Reporting Rule: Revisions and
Confidentiality Determinations for Petroleum and Natural Gas
Systems, 89 FR 42062 (May 2024).
\2\ Final Standards of Performance for New, Reconstructed, and
Modified Sources and Emissions Guidelines for Existing Sources: Oil
and Natural Gas Sector Climate Review, 89 FR 16820 (March 2024).
---------------------------------------------------------------------------
Following requests for comment in the notice of the 2023 proposed
rulemaking for Subpart W,\3\ the EPA received numerous comments
requesting that the use of advanced measurement technologies be allowed
to quantify emissions from other sources beyond other large release
events in Subpart W. In response to these comments, EPA reviewed remote
sensing and in situ advanced measurement approaches (including both
intermittent and continuous monitoring approaches) that utilize
information from satellite, aerial, drone, vehicle, and stationary
platforms to detect and/or quantify methane emissions from oil and gas
operations for their potential use in Subpart W reporting. As a result
of this review and in response to comments on the proposed Subpart W
rule, in May 2024, EPA finalized additional options within Subpart W to
use advanced measurement technologies to measure data that are inputs
to emission calculations for flares and well completions and workovers,
in addition to the proposed use of advanced measurement technologies to
quantify emissions from other large release events and/or estimate the
duration of such events.
---------------------------------------------------------------------------
\3\ Proposed Greenhouse Gas Reporting Rule: Revisions and
Confidentiality Determinations for Petroleum and Natural Gas
Systems, 88 FR 50282 (August 2023).
---------------------------------------------------------------------------
As EPA acknowledged in the final Subpart W rule, advanced
measurement technologies are developing rapidly and are particularly
well-suited for detecting and quantifying large and discrete emissions
events, such as other large release events. Based on EPA's assessment
of the strengths and limitations of advanced measurement technologies
at the time of finalizing the Subpart W rule, however, EPA limited the
use of these technologies in annual GHG reporting to certain specific
roles identified in the final rule.\4\
---------------------------------------------------------------------------
\4\ Final Greenhouse Gas Reporting Rule: Revisions and
Confidentiality Determinations for Petroleum and Natural Gas
Systems, 89 FR 42062 (May 2024).
---------------------------------------------------------------------------
EPA has also sought comment on how methane monitoring technologies
might enhance emission estimates for other industrial sectors covered
under the GHGRP, specifically for MSW landfills under 40 CFR part 98
Subpart HH (Subpart HH). In a May 2023 notice of proposed rulemaking,
EPA requested examples of methane data collected from available
monitoring methodologies and how such data might be incorporated into
quantifying annual emissions.\5\ Although the EPA did not take final
action to incorporate advanced measurement technologies in the April
2024 final rule for the reasons described therein,\6\ including
information in comments received noting limitations in existing
technologies, EPA has continued to review ways to incorporate the use
of advanced measurement technologies into the emissions reporting for
MSW landfills for GHGRP reporting purposes under Subpart HH.
---------------------------------------------------------------------------
\5\ Proposed Revisions and Confidentiality Determinations for
Data Elements Under the Greenhouse Gas Reporting Rule, 88 FR 32852
(May 2023).
\6\ Final Revisions and Confidentiality Determinations for Data
Elements Under the Greenhouse Gas Reporting Rule, 89 FR 31802 (April
2024).
---------------------------------------------------------------------------
Based on these reviews, EPA recognizes that advanced measurement
technologies, and their use for annual quantification of methane
emissions, are evolving rapidly. EPA is committed to transparent and
continual improvements to its programs to ensure reporting is accurate
and complete. There are four key considerations associated with
expanding the use of advanced measurement technologies to quantify
annual methane emissions \7\ under the GHGRP in a robust, transparent,
accurate, standardized, and verifiable way:
---------------------------------------------------------------------------
\7\ Current GHGRP reporting requires quantification of methane
emissions at the equipment-, process-, or facility-level. For
example, under Subpart W emissions are quantified and reported for
specific equipment types, such as pneumatic controllers. For Subpart
HH, emissions are quantified and reported at the facility-scale,
which includes the total surface area of the landfill, or for
specific processes such as landfill gas collection and control
systems.
---------------------------------------------------------------------------
[[Page 70179]]
(1) How to translate the measurement data provided by different
types of advanced measurement technologies (e.g., methane plume images,
satellite retrievals of column methane mixing ratios, ambient methane
concentrations) into total tons of methane emissions.
(2) How to extrapolate methane emissions from discrete and
intermittent observations into total methane emissions throughout the
year (with a specific level of accuracy) and attribute these emissions
to a specific equipment type, process, or facility.
(3) How to identify, attribute, and quantify methane emission
events that are below a technology's detection limit, in order to
estimate total equipment-, process-, or facility-level emissions
throughout the year.
(4) How to set detection, quantification, attribution,
verification, and uncertainty criteria and/or protocols for different
types of advanced measurement technologies to ensure implementation
into the GHGRP in a manner that is applicable to different
infrastructures and environmental conditions across the U.S. (e.g.,
topographies, climates, facility types and layouts).
As technologies continue to rapidly advance to meet these needs,
EPA is issuing this RFI to the public to obtain information about
currently available advanced and emerging methane measurement
technologies, and how these technologies could be used to quantify
annual methane emissions from the oil and gas and MSW landfill industry
segments at the equipment-, process-, or facility-level for GHGRP
reporting purposes. The following questions are aimed to address the
key considerations outlined above and have been organized into the
following categories: quantification, attribution, and implementation.
EPA believes that standards or protocols could help ensure the use
of advanced measurement technologies to quantify annual methane
emissions is implemented in a transparent and standardized manner.
Furthermore, EPA anticipates that annual quantification approaches may
be specific to an emission source, facility type, or type of
technology. Therefore, a potential standard or protocol might be
specific to a type of methane source (e.g., hydrocarbon liquid storage
tanks, landfill working face) and a specific measurement approach
(e.g., drone, aircraft, vehicle-based, or multi-platform based). For
example, for a specific type of source, a potential standard or
protocol might include a detection limit below a certain methane
emissions rate threshold, a sampling frequency and duration (e.g., 1
overpass weekly) to ensure representative sampling of operating
activities throughout the reporting year, the inclusion of specific
ancillary data (e.g., wind speed and direction), and the use of a
transparent and peer-reviewed methodology (e.g., inverse analysis,
statistical sampling) to quantify the annual total methane emissions to
within a specified level of accuracy (e.g., 90%). To the extent that
information provided in response to the questions below are specific to
a particular emissions source, facility type, or technology type,
please indicate the applicability in the comments provided.
II. Questions
1. Quantification of Annual Emission Rates
EPA is requesting information on issues related to the
quantification of methane emissions using currently available advanced
measurement technologies, including: (1) detection and quantification
of methane emission rates; (2) approaches for extrapolating
observation-based methane emission rates to estimate annual total
emissions; and (3) approaches for quantifying annual total methane
emissions for sources that emit at rates below technology minimum
detection thresholds. Detailed questions on each topic are listed
below. Please provide detailed answers and citations to relevant
resources.
a. Detection and Quantification of Atmospheric Methane Emission Events
From Advanced Measurement Technologies
Advanced technologies for methane detection, such as instruments
deployed on satellite, aircraft, or in the form of continuous monitors,
can be used to detect methane emissions. These technologies do not
directly quantify methane emission rates but require additional
analytical tools and methods to transform the raw sensor measurements
(e.g., change in light attenuation) into quantified methane emission
rates (e.g., kg/hour) associated with each observation. Quantification
approaches can include but are not limited to the inverse analysis of
observed concentrations, the use of dispersion modeling, co-emitted
tracer releases, or mass balance approaches. Based on the wide variety
of detection and quantification approaches currently available, EPA
requests comment on the following:
i. What advanced measurement technologies are currently available
that can provide quantified methane emission rates using transparent,
open-source, and standardized methodologies? What are the specific
quantification approaches that have been used with these technologies,
and how have these methodologies been demonstrated and validated? How
can these technologies and quantification methodologies be used to
provide annual data in a consistent manner for each future year of
GHGRP reporting? Are there specific detection and quantification
approaches or methodologies that EPA should or should not consider?
ii. What performance metrics and threshold(s) related to
quantification would be appropriate to apply to advanced measurement
technologies for their incorporation into the GHGRP? For example,
should EPA consider: thresholds for the methane detection limit (e.g.,
minimum emissions leak rate), thresholds for the probability of
detection (e.g., rate of false positives or negative detections),
specific levels of accuracy for quantification, specific measurement
frequencies, or other? What would be a feasible approach for developing
these thresholds and metrics?
iii. Should quantification approaches be limited to the use of
specific methodologies (e.g., inverse analysis, mass balance) or
specific approaches for using ancillary datasets (e.g., standardized
interpolation of wind field products)?
iv. Are there ongoing efforts outside of EPA to develop standards
or protocols for methane emissions detection and quantification from
advanced measurement technologies that would address any of the
questions raised in this RFI? If so, please specify which efforts and
which question(s) can/will be answered and when these standards or
protocols will be publicly available.
b. Extrapolating Quantified Methane Emission Rates To Calculate Annual
Emissions for GHGRP Reporting Purposes
Different advanced measurement technologies provide data at
different sampling frequencies (e.g., continuous to weekly) and
durations (e.g., seconds to hours). Depending on the type of technology
and emissions source sampled, different approaches have been used to
extrapolate observation-based methane emission rates to estimate total
annual emissions for a specific region, facility, or site. These
approaches often require additional information on the frequency and
duration of the sampled emission events, information on the population
of sampled emission sources, site-specific
[[Page 70180]]
operational activities, or statistical analytical approaches. EPA seeks
comment on the following:
i. What advanced measurement technologies are currently available
that can provide annual total methane emission estimates for specific
regions, facilities, processes, or equipment-level sources, that use
transparent, open-source, and standardized methods? Are these
technologies applicable across the entire U.S. and could they provide
annual data in a consistent manner for each future year of GHGRP
reporting? Are there specific annual extrapolation approaches or
methodologies that EPA should or should not consider?
ii. What accuracy or uncertainty metrics would be appropriate for
GHGRP reporting purposes? For example, what level of accuracy in
reported annual methane emissions should advanced measurement
technologies be required to meet? What sources of uncertainty are
necessary to consider? Are there other specific quality assurance or
quality control markers that should be considered to ensure that annual
estimates represent the methane emissions from all operational
activities throughout the reporting year, such as specific measurement
frequencies or duration? What would be a feasible approach for
developing these thresholds and metrics?
iii. To what extent should standards and protocols be specific to
the type of methods and ancillary data used (e.g., statistical
approaches), and to what extent should standards and protocols
simultaneously consider the specific type of emission sources being
sampled (e.g., large unintended vs. small routine emissions event)?
c. Quantifying Annual Methane Emissions From Emissions Sources Below
Detection Limits of Advanced Measurement Technologies
Different advanced measurement technologies also have different
detection thresholds (e.g., ~1 kg/hr to above 100 kg/hr), in part
dependent on the distance of the instrument from the source (e.g.,
typically larger detection limit for instruments on satellites compared
to aircraft), instrument type, and sampling strategy. In the current
GHGRP, a significant number of sources emit methane at rates below
these typical detection limits (e.g., a component leak will typically
emit at rates significantly below 1 kg/hr). To account for methane
emissions from these additional sources, various methodologies and
statistical approaches have been developed to estimate total annual
emissions to complement the data collected from advanced technology
measurements. EPA seeks comment on the following:
i. What methodologies are currently available for integrating
estimates of methane emissions for those sources emitting below
technology detection thresholds in an open-source, transparent, and
standardized way? Can these methodologies provide annual data in a
consistent manner for each future year of GHGRP reporting? Are there
specific approaches or methodologies that EPA should or should not
consider?
ii. Should these quantification approaches be limited to the use of
specific methodologies (e.g., Monte Carlo method) or specific ancillary
datasets (e.g., the use of standardized infrastructure or operator
data)?
2. Attribution
EPA is requesting comment and information regarding attribution of
quantified methane emissions (from discrete events or annual totals) to
specific GHGRP facilities, sites, or sources.
In addition to differences in temporal resolution, advanced
measurement technologies have spatial resolutions that can range from
kilometers (e.g., satellite) to site or individual equipment scales
(e.g., ground-based sensors). There are different approaches for
attributing observed events to a specific equipment type, process, or
facility depending on the specific type of technology used and sampling
distance from the emissions source. These approaches often require
ancillary information such as infrastructure data, site operator data,
or meteorological data such as wind speed and direction. EPA seeks
comments on the following:
a. What methodologies are currently available that can attribute
quantified methane emission events to specific equipment types (or
additionally, specific regions, facilities, or processes) using
transparent, open-source, and standardized methods? Are there specific
attribution approaches or methodologies that EPA should or should not
consider?
b. What accuracy or uncertainty metrics would be appropriate for
GHGRP reporting purposes? For example, what level of confidence in the
source attribution would be necessary for advanced measurement
technologies to meet for GHGRP reporting purposes? What would be a
feasible approach for developing these thresholds?
c. To what extent would standards and protocols need to be specific
to the type of methods and ancillary data used (e.g., infrastructure
datasets) or the type of emission source sampled (e.g., large
unintended vs small routine emissions event)?
3. Implementation
EPA is requesting comment and information on issues related to the
implementation of advanced measurement technologies into the GHGRP.
Implementation considerations include the need for quantifying
annual total methane emissions from oil and gas and MSW landfill
applicable sources across the U.S. in a transparent and standardized
way, validation and verification of the reported data, and additional
potential uses of advanced measurement technologies for the GHGRP. EPA
also requests information on additional data that could be reported for
the verification of methane emissions estimates produced using advanced
measurement technologies.
a. Structure of Approaches or Protocols
i. What form would standard method(s) or protocol(s) need to take
to ensure that advanced measurement technologies provide annual total,
source-specific, methane emissions in a transparent and standardized
way? For example,
(1) To what extent should standards and protocols be specific to
the type of methods used (e.g., satellite, aircraft, ground-based)? In
addition, would different standards or protocols be necessary for
sampling approaches using single platform vs. multi-platform
measurements? Could standard methods be developed to be technology
agnostic?
(2) To what extent could standard method(s) be developed to be
source agnostic? For example, would standards need to be specific to
the type of equipment, process, or emission source sampled (e.g.,
tanks, flares, pneumatic devices, landfill working face), or could a
set of standard(s) be developed to be more broadly applicable across
different GHGRP industry segments (e.g., oil and gas operations and
landfills)? Alternatively, would different standards be necessary for
different types of methane emission events sampled (e.g., large
unintended vs small routine emissions events)?
b. Verification and Validation of Annual Source-specific Methane
Emission Quantification Methods Using Advanced Measurement Technologies
for GHGRP Reporting Purposes
i. Are there approaches currently available that could be used to
verify that advanced measurement technologies meet specific standards
(e.g., independent blind studies,
[[Page 70181]]
deployment of calibration standards, other)?
ii. Is it necessary to limit the applicability of advanced
measurement technologies to environmental and site conditions that have
been previously validated? For example, if an advanced measurement
technology has been validated through blind control release testing
during which wind speeds ranged from 0.5 to 10 m/s, should the
technology be limited to measurements within this range of wind speeds?
What form of validation could be used to demonstrate whether a
technology is applicable across environmental conditions outside of
their tested ranges?
iii. Are there specific types of operator- or facility-specific
information that would be useful for improving or validating annual
methane emissions quantification or source attribution from advanced
measurement technologies?
c. Other Considerations Related to the Use of Advanced Measurement
Technologies for GHGRP Reporting Purposes
i. What (if any) are the current barriers or limitations to using
advanced measurement technologies beyond what is currently allowed
under the GHGRP to quantify annual equipment-level methane emissions at
scale in the U.S.?
ii. What are the cost considerations for implementing different
advanced measurement technologies to quantify annual, equipment-,
process-, or facility-level methane emissions for GHGRP reporting
purposes? If available, costs should be provided in a manner that can
be scaled up to different implementation approaches (e.g., cost per
site, cost per area covered).
iii. How are factors such as measurement and analysis cost,
complexity, or time burden relevant for determining whether advanced
measurement technologies may be appropriate for annual GHGRP
application?
iv. Other than methane emissions detection and quantification, and
establishing the duration of emission events as permitted under Subpart
W for Other Large Release Events, are there additional ways in which
advanced measurement technologies could be used to support
quantification and reporting of equipment-, process-, or facility-level
methane emissions to the GHGRP (e.g., as a method to identify changes
in operating conditions, to supplement specific reported data
elements)?
Sharyn Lie,
Director, Climate Change Division.
[FR Doc. 2024-19403 Filed 8-28-24; 8:45 am]
BILLING CODE 6560-50-P