Workshop G
Air Permitting … Major New Source Review (NSR) Changes Impacting How You Do Business in Ohio
Wednesday, July 25, 2018 2:45 p.m. to 4:15 p.m.
Workshop G Air Permitting Major New Source Review (NSR) Changes - - PDF document
Workshop G Air Permitting Major New Source Review (NSR) Changes Impacting How You Do Business in Ohio Wednesday, July 25, 2018 2:45 p.m. to 4:15 p.m. Biographical Information Mike Burr, Managing Consultant Trinity Consultants 3401
Air Permitting … Major New Source Review (NSR) Changes Impacting How You Do Business in Ohio
Wednesday, July 25, 2018 2:45 p.m. to 4:15 p.m.
Biographical Information Mike Burr, Managing Consultant Trinity Consultants 3401 Enterprise Parkway, Suite 340, Beachwood, Ohio 44122 216.278.0500 Fax: 614.433.0734 mburr@trinityconsultants.com Mike currently operates as a Managing Consultant in Trinity’s Cleveland, Ohio office providing support to numerous industries across Ohio, West Virginia, and Michigan. His work involves air dispersion modeling, state and federal air construction permitting, development of emissions inventories, and comprehensive Title V compliance management. Mike serves as a lead air dispersion modeler in Ohio and has specialized experience performing and managing complex air dispersion modeling analyses in support of state and federal construction permits. Mike received a Bachelor’s degree in meteorology from Ohio University and a Master’s degree in atmospheric science from North Carolina State University. William H. Haak, Founder, Haak Law LLC, 12595 Bentbrook Dr., Cleveland, OH 44026 216.772.3532 whh@haaklawllc.com William H. Haak is the Founder of Haak Law LLC – an environmental, health & safety legal and consulting firm based in Cleveland, Ohio. He has nearly 20 years of experience in occupational safety law and worker safety, and nearly 25 years of experience in environmental law (including extensive experience in air pollution control law and multi-media environmental compliance).
the EHS field (plus security and crisis management).
Reserve University School of Law (J.D. with an emphasis on litigation and trial practice). Following law school, he worked as an Assistant Attorney General in the State of Ohio Attorney General’s Environmental Enforcement Section. As counsel to Ohio EPA, Mr. Haak’s practice was focused primarily on civil and administrative air pollution control cases. During his time with the Attorney General’s Office, Mr. Haak resolved civil environmental enforcement actions resulting in civil penalties totaling approximately $4 million. Prior to forming Haak Law LLC, Mr. Haak was Senior EH&S Counsel for General Electric. He supported GE’s Appliances and Lighting Businesses and was engaged in complex air permitting issues for other GE businesses nationwide. Mr. Haak has also been Associate General Counsel – EH&S for Hexion Specialty Chemicals in Columbus, Ohio, and Senior Regulatory Law Counsel for Owens Corning in Toledo, Ohio. He served overseas in the former Soviet Union (Ukraine) as an Environmental Enforcement Specialist with the American Bar Association’s Central & East European Law Initiative ("ABA/CEELI"). Haak is a frequent lecturer to attorneys, engineers, and environmental professionals on topics concerning federal and state air pollution law. In addition, he has taught as an adjunct faculty member at the University of Central Florida in Orlando and Columbus State in Columbus, Ohio. Since 2005, Haak has taught classes focusing on Air Pollution Law and Occupational Safety and Health Law at The University of Toledo College of Law as an Adjunct Professor.
Biographical Information Robert F. Hodanbosi, Chief Ohio EPA, Division of Air Pollution Control Lazarus Government Center, 50 West Town Street, Columbus, OH 43215 614.644.2270 Fax: 614.644.3681 bob.hodanbosi@epa.state.oh.us Bob Hodanbosi became chief of the Division of Air Pollution Control (DAPC), Ohio Environmental Protection Agency (Ohio EPA) in September 1992. His current duties include being responsible for the air pollution control program for the state of Ohio and development of the programs needed to comply with the Clean Air Act Amendments. In 2004, Bob was selected to represent state permitting authorities on the Title V Permit Performance Task Force that was formed by the U.S. EPA's Clean Air Act Advisory Committee. Bob has also had the opportunity to testify at U.S. House and Senate committees on Clean Air Act implications for facilities in Ohio. From May 1987 to September 1992, his position was assistant chief of DAPC and manager of the Air Quality Modeling and Planning Section, DAPC, Ohio EPA. From April 1978 to May 1987, as manager of the Air Quality Modeling and Planning Section, his main duties included: development of the technical support for air pollution control regulations for criteria air pollutants; atmospheric dispersion modeling; air quality designations under Section 107 of the Clean Air Act and, development of new source review procedures. Since the 1980's, Bob has represented Ohio EPA on the Ohio Coal Development Office, Technical Advisory Committee. From January 1977 to April 1978, his position was supervisor of the Environmental Assessment Unit, DAPC, Ohio EPA. The main responsibilities of this position involved the supervising of all air quality evaluation and atmospheric dispersion modeling activities for DAPC. From June 1973 to December 1976, he held a position in the Northeast District Office/Engineering Services Section, DAPC, Ohio EPA. The main function of this position involved the engineering review of air pollution permit applications. Bob is a member of the American Institute of Chemical Engineers and Air & Waste Management Association and is registered as a Professional Engineer in the state of Ohio. Bob has lectured extensively on topics relating to the requirements under the Clean Air Act and the controls needed to meet air quality standards. Bob received his Masters of Science degree in Chemical Engineering at the Cleveland State University in 1977, and a Bachelor in Chemical Engineering at the Cleveland State University in
Ohio State University.
28th Annual Conference on Air & Water Permits – Environmental Permitting in Ohio
Workshop G – Air Permitting … Major New Source Review (NSR) Changes Impacting How You Do Business in Ohio
July 25, 2018
HAAK LAW LLC
Environmental, Health & Safety Legal and Consulting Services
Environmental Permitting in Ohio Workshop G
Bob Hodanbosi Ohio EPA Division of Air Pollution Control July 25, 2018
What is Major New Source Review
(NSR)?
Attainment/Nonattainment Areas Prevention of Significant Deterioration
(PSD) Permitting
Nonattainment New Source Review
(NNSR) Permitting
Bonus Material
Permits required under the Clean Air Act: Major New Source Review (NSR) includes:
attainment areas
Can include both “new major” or “major modification” If the emissions are large enough (over trigger
levels), then a “Major New Source” permit is required
Criteria pollutants are classified as attainment,
unclassifiable or nonattainment
An attainment area is designated as “attainment” or
“unclassifiable” for the National Ambient Air Quality Standards (NAAQS).
A nonattainment area is one officially designated as
nonattainment
An area can be attainment/unclassified for some
pollutants, and nonattainment for others.
Geographic areas where U.S. EPA has
designated the area as attainment or non classifiable.
Applies for only the attainment pollutant and
precursor emissions (VOCs for ozone, NOx and SO2 for PM2.5).
Some areas violate standards and are not yet
designated nonattainment - PSD still applies
Geographic areas where U.S. EPA has
designated the area as nonattainment.
Applies for only the nonattainment pollutant and
precursor emissions.
Official designation determines regulatory path -
If nonattainment areas attain standards, redesignation process is slow, NNSR applies until area designated to attainment
Pollutant Primary Source Attainment Status Carbon Monoxide cars and trucks Attainment Nitrogen Oxides any type of combustion, utilities, industrial boilers, vehicles Attainment Lead individual industrial facilities Isolated maintenance Sulfur Dioxide coal fired power plants Isolated nonattainment Ozone sources of NOx and hydrocarbons, including cars, trucks, utility boilers, painting operations, refineries Attainment for 2008 standard; Columbus, Cincinnati, and Cleveland areas nonattainment for 2015 standard Particulate Matter coal fired boilers, cement plants, steel making
Lorain/Cuyahoga Counties nonattainment (in process of redesignation)
Sulfur Dioxide Nonattainment areas PM2.5 Nonattainment Area
8-hour standard – 0.70 ppm
(avg. of 4th high over 3-yrs)
June 4, 2018 – US EPA
finalized non-attainment areas (effective August 3, 2018)
due August 3, 2020
marginal non-attainment (attainment date- August 3, 2021)
Implementation Timeline
PSD Goals Important Terms Applicability Requirements of PSD
Designed to protect air quality
in attainment areas
Allow economic growth Protect public health and
welfare
Preserve, protect, and
enhance air quality in special areas
Attainment
Determine if the proposed source is a major stationary
source for any attainment area pollutants (100, 250 ton thresholds)
If any of the attainment pollutants trip the major
stationary source thresholds, then the source is considered a major stationary source for PSD
Determine if GHGs are above 75,000 CO2 – if yes, PSD
for GHGs
PSD cannot be triggered by GHGs alone
First, determine if the existing facility is a major
stationary source for any attainment area pollutants (100, 250 ton thresholds)
Second, determine that a physical change or change
in the method of operation is occurring
Third, do the two-part emissions increase test for
each pollutant
Pollutant and Emissions Rate Carbon monoxide: 100 tons per year (tpy) Nitrogen oxides: 40 tpy Sulfur dioxide: 40 tpy Particulate matter: 25 tpy of particulate matter emissions PM10: 15 tpy PM2.5: 10 tpy of direct PM2.5 emissions; 40 tpy of sulfur dioxide emissions;
40 tpy of nitrogen oxide emissions unless demonstrated not to be a PM2.5 precursor under paragraph (b)(50) of this section
Pollutant and Emissions Rate
Ozone: 40 tpy of volatile organic compounds or nitrogen oxides Lead: 0.6 tpy Fluorides: 3 tpy Sulfuric acid mist: 7 tpy Hydrogen sulfide (H2S): 10 tpy Total reduced sulfur (including H2S): 10 tpy Reduced sulfur compounds (including H2S): 10 tpy
Check each regulated NSR pollutant separately First, determine if the increase associated with the modification
qualifies as a significant emissions increase
Second, determine if the net emissions increase for that
pollutant is significant
If PSD is triggered for modification, then GHGs must be
calculated to determine if above 75,000 TPY threshold
PSD cannot be triggered by GHGs alone
Net emissions increase can get complex Important to verify with DO/LAA Don’t want to find out late in the permit process
that your evaluation was incorrect
Fugitive emissions means those emissions that cannot
reasonably pass through a stack, chimney, vent or
Examples:
quarries
and flanges at refineries and oil processing equipment
They are included in a source’s PTE to the extent that
they can be quantified, if they are present at:
8/7/80
If a source has been determined to be major for that
pollutant, they are included in any subsequent analysis (e.g. air quality impact)
28 Source categories are general, not specific to NSPS
Emissions which, although associated with the
construction or operation of a source, are not emitted from the source itself.
For example, increased rail traffic from new refinery
that will obtain crude by rail
They do not count toward PTE, but must be
considered in the PSD air quality analysis if PSD is required.
Typically not an issue
Employ BACT Ambient monitoring Emissions modeling Other impacts analysis
Best Available Control Technology means an
emissions limitation … maximum degree of reduction….each regulated NSR pollutant…which the director…taking into account energy, environmental and economic impacts and other costs determines is achievable…
Can use production processes or available methods,
systems and techniques, including fuel cleaning or treatment or innovative fuel combustion techniques for control
1.
Top-Down Process
2.
Identify all control technologies
3.
Eliminate technically infeasible options
4.
Rank remaining control technologies by control effectiveness
5.
Evaluate most effective controls and document results
6.
Select BACT
*See additional material at the end of the presentation.
Greenhouse Gas Emissions (GHGs) come into play as part of PSD process – decided by U.S. Supreme Court
Must be a PSD “anyway” source – source is
Requires application of BACT – focus has been
Rules require preconstruction monitoring if modeling
shows impacts above monitoring trigger levels
Monitoring trigger levels – 3745-31-13(H) or EG 69 Monitoring required for one year (mostly) Court decision on PM2.5 changes ground rules for that
pollutant
D.C. Court of Appeals determined that
Significant Impact Levels (SILs) not supportable
Deminimus value would be okay – just not
manner U.S. EPA adopted PM2.5 SIL
US EPA issued new guidance on SILs U.S. EPA adopted Significant Monitoring
Concentration (SMC) of 0.0 ug/m3 for PM2.5
Important ramifications for new projects
If monitoring is needed,
existing monitors may be sufficient to fulfill requirement
Ohio is a large network of
monitors in near urban areas for most pollutants
Nitrogen dioxide is
exception – only a few
Rules require air quality impact analysis that
demonstrates:
concentration (typically < ½ available increment)
Other Impacts Analysis
What is a regulated NSR pollutant? NAAQS Pollutant (SO2, Ozone, PM, PM-10, NOx,
PM2.5, CO, Pb)
Precursor pollutants
Only covers NAAQS and precursor pollutants,
different than for PSD
LAER - Lowest Achievable Emission Rate Emissions Offsets Net air quality benefit from offsets Certify all major operations owned by the source in the
state are in compliance with SIP (or on an enforceable schedule)
A new source/major modification will be subject to NA
NSR in Ohio if:
Major Source) any criteria pollutant ( or precursor) for which the area is designated as nonattainment, OR
which results in a significant increase (see Significance Levels table) in emissions of a pollutant for which the source is major and the area is designated nonattainment.
Marginal Moderate and Basic Serious Severe Extreme Ozone (NOx and VOCs are precursors) 40 40 25* 25* any CO
50
15
(Nox and SO2 are precursors)
40 *when aggregated with all other net increases 25 tpy in emissions from the source over any period of 5 consecutive years
LAER is the most stringent emission limitation based on
either: 1) the most stringent limitation achieved in practice by class or source category (without taking into account economic, energy, or other environmental factors), OR 2) the most stringent limitation in any SIP for that class
LAER cannot be less stringent than any applicable
NSPS limit.
LAER is an emissions rate specific to each emissions
unit.
This emissions rate may result from a combination of
emissions-limiting measures such as:
A new or modified source is required to “offset”
any increased emissions (it generates) with a decrease elsewhere in the same nonattainment area.
The offset provision shifts the burden of
accommodating new growth in NA areas to new
allowed within a given area.
Obtaining offsets is generally done by purchasing
emission credits from another source or combination
area, to offset the increase in emissions from the new source/modification.
The purpose of the offsets is to allow the area to move
towards attainment while still permitting some industrial growth.
See Finding Offsets additional material
Offset ratios need to be greater than 1:1. Offset ratios for basic are 1.1:1 in basic areas, 1.15:1 for
moderate areas
Offsets should be located in the same nonattainment area,
Offsets must be in the permit or a SIP revision. Offsets must be practically enforceable.
Emission reductions required by the State
Implementation Plan (SIP) or a state or federal consent decree
The difference between the SIP and the NSPS if
it is applicable to the source
The offsets must produce a “Net Air Quality
Benefit” (for the area affected by the new/modified source)
This is required so that after the source is built, air
quality is better than before the source began
Modeling demonstration required for some
pollutants (SO2, NOx)
All major sources owned or operated by the
facility in the state must be in compliance with the State Implementation Plan (SIP)
Rules allow facility to be on an enforceable
schedule or consent decree to achieve compliance
An analysis by the source owner of:
Analysis for such proposed source must demonstrate
that benefits significantly outweigh:
Don’t forget about “netting” for both PSD and NNSR If “internal” offsets (offsets at that plant) can be
generated; “netting” will probably work
Frequently used on expansions or replacements, but
does not work for new facilities
Questions…
Potential to emit means the maximum capacity of an
emissions unit or stationary source to emit an air pollutant under its physical and operational design.
PTE can be limited through federally enforceable
means, such as:
combusted or stored
What is a regulated NSR pollutant? NAAQS and constituents or precursors Section 111 pollutants (NSPS) Title VI Class I or II (ozone depleting) Other CAA regulated except HAPs (unless
constituents or precursors)
Greenhouse gas emissions
Emissions Units
belonging to the same industrial grouping or support,
Located on one or more
contiguous or adjacent properties, and
Under common control.
In the same industrial group (SIC
Code)
Under the control of same owner Located on contiguous or adjacent
properties – for oil and gas within ¼ mile of each other
VOC for ozone Don’t count quantifiable fugitive unless on
the list
List is not specific to NSPS If the change by itself is major at a non-
major source, then the project is a major stationary source
4 page rule definition (3745-31-01(LLL)) Physical change in or change in the method of
would result in:
AND
pollutant
The change itself must be above the
significance levels, AND
The net change must be above the
significance levels for the project to be a major modification
Both statements must be true to be a major
modification (when not netting)
Significant VOC = significant ozone Calculation method for significant emissions
increase is different for existing vs new
Physical change or change in the method
qualifiers
PAL qualifier
Should be comprehensive; source should not
yet discount options because of infeasibility
Source should consider add-on controls and
inherently lower-emitting processes and practices
Scope is not limited by other regulations or by
national boundary
Step 1 (cont) Innovative technologies may be considered; technology transfer must be
considered
RBLC:
BAT: needs updated link
Install and Permit to Operate) files)
If a control technology has already been installed
and successfully operated on the type of source under review, it’s technically feasible (unless there are obstacles at the source that justify infeasibility).
Otherwise, source must consider whether the
technology is:
Rank from most to least effective in terms of
emission reduction.
If a control technology has a range of
performance, select the reduction level that has been achieved at other sources.
Weighing of energy, environmental and economic factors Energy Impacts Analysis Source should determine whether the control
technology’s energy requirements would result in significant or unusual energy penalties or benefits
Should only consider direct energy consumption May involve fuel scarcity
Environmental Impacts Analysis Concentrates on non-air quality impacts, such
as solid/hazardous waste, water effluent, visibility, or emission of unregulated pollutants.
Significant or unusual collateral impacts may be
reason for disqualifying a control technology.
Economic Impacts Analysis (Cost analysis) Cost effectiveness: dollars per ton reduced A technology may be rejected if the cost is
disproportionately high when compared to recent BACT determinations
BACT analysis may involve vendor-supplied estimates, cost
manuals developed by EPA, data from trade publications, etc.
(Annualized Cost)/(Baseline emission rate -
Control option emission rate)
construction, start-up, performance testing)
Annual cost estimate may include:
recovery)
Capital charges (taxes and insurance, capital
recovery factor, interest on working capital)
Engineering Guide #46 EPA Air Pollution Control Cost Manual
http://www.epa.gov/ttncatc1/products.html#cccinfo
Need help? Talk to NSR contact.
Existing Fac.1 Increase Net Increase Trigger PSD? 251 t/y NOx2 35 t/y 45 t/y 40 t/y No 240 t/y VOC 45 t/y 35 t/y 40 t/y No 15 t/y PM10 5 t/y 20 t/y 15 t/y No 50 t/y SO2 45 t/y 45 t/y 40 t/y Yes
1 Assume facility is located in an attainment area for all of the
above listed pollutants.
2 This emission rate makes it a “major stationary source.”
PSD permit applicant must prepare an analysis on any
impairment to visibility, soils and vegetation
Applicant must prepare an analysis of the air quality
impact as a result of the general commercial, residential, industrial or other grown associated with the project
Rarely significant
Based on an inventory of the soils and
vegetation types found in the area, including all vegetation of commercial or recreational value
Rarely significant but can be for pollutants like
hydrogen fluoride
Affects projects that are located near or impact Class I areas Class I areas are places like national parks No Class I areas in Ohio Closest is Dolly Sods Wilderness area in WV Rarely significant but could be for large projects like power plants
Contact the DO/LAA and ask them for recent shutdown
sources in their area.
Obtain copy of the emissions inventories for past years.
Determine if sources have been shutdown.
Contact local chamber of commerce to find closures Contact the Ohio EPA permit staff and ask about
available Emission Reduction Credits in bank
Ohio EPA developed rules to allow for emission banking Allows permanent emission reductions to be formally
recognized
Credits are posted on internet so that interested parties can
see what is available in the area
For more information contact Sudhir Singhal –
sudhir.singhal@epa.ohio.gov
Many more nonattainment areas for ozone, SO2,
PM2.5
Want to attract new business, expansions of current
business
Ohio EPA bank designed to assist development in
nonattainment areas
bob.hodanbosi@epa.ohio.gov
Major New Source Review (NSR) Overview of Important Changes
July 25, 2018
Mike Burr Managing Consultant Trinity - Cleveland
mburr@trinityconsultants.com 3401 Enterprise Parkway, Suite 340| Beachwood, Ohio 44122 Office: (216) 278-0500
˃ Air dispersion modeling required to demonstrate
compliance with NAAQS and PSD Increments during major NSR process
Revised Appendix W published on January 17,
2017
♦Effective 5/22/2017
˃ Wide ranging changes
NO2 modeling options Treatment of secondary PM2.5 and ozone Regional source considerations Many others…
˃ Ohio EPA released draft Engineering Guide #69
Comments due July 27, 2018 Final guidance expected later this year
˃ Changes generally intended to align EG#69 with
recent revisions to Appendix W
˃ Addresses OAC 3745-31-01(SSS)(1)(b)
Triggering modeling without an emission
increase
˃ Revised definition of ambient air? ˃ Final Modeling Emission Rates for Precursors
(MERPs) guidance
No significant changes expected from draft
˃ Draft Ozone/PM2.5 modeling guidance expected
this summer
Replace 2014 guidance document
˃ Guidance/policy documents on these three (3)
expected this summer (?)
˃ New Source Review Preconstruction Permitting
Requirements: Enforceability and Use of the Actual-to- Projected-Actual Applicability Test in Determining Major Modification Applicability, Pruitt, 12/12/2017
˃ Project Emissions Accounting Under the New Source
Review Preconstruction Permitting Program, Pruitt, 03/13/2018
˃ Meadowbrook Energy and Keystone Landfill Common
Control Analysis, Wehrum, 04/30/2018
˃ Applicability of Major NSR for existing sources is a 2-step
process:
Step 1: Project emission increase
Step 2: Net emissions increase (commonly referred to as “netting”)
˃ USEPA has historically maintained that emission decreases
associated with a project may not be considered under Step 1 (referred to as ‘project netting’)
Full 5-year netting evaluation required to account for any decrease, even those from decommissioning unit as part of project under consideration
˃ Practical Implementation of this interpretation has
resulted in significant delay and even prevention of certain projects from moving forward
˃ March memo documents new EPA
interpretation
Based on plain language of CAA, which indicates
that Congress intended to apply NSR to changes that increase actual emissions (where actual emissions increase would be a function of both project-related increases AND decreases)
˃ Decreases may now be considered in Step 1
˃ Project:
Modify emission units P001, P002: +24 tons NOX
Install new emission units B001 +30 tons NOX
Projected decrease at P003, P004
˃ Step 1 Increases
No Project netting: 54 tons
♦ Onto step 2! ♦ Other increases in
contemporaneous period?
Project netting: 35 tons
♦ Done!
Contemporaneous Period - 5 years
Projected Start Construction
Projected Start Operation
˃ Must be causal link between physical/operational
change and change in emissions
˃ Facility responsible for defining project scope
May not seek to circumvent NSR
˃ Decreases need not be creditable or enforceable to
be considered in Step 1
However, decreases considered in Step 2 must be both
˃ Caveats:
Local agencies may take more stringent interpretation than federal guidance
Permit engineers may not be receptive to idea of accounting for decreases without method of enforceability
˃ When should sources be considered a ‘single
stationary source’ for Title V or NSR permitting purposes?
1.
The stationary sources are located on one or more contiguous or adjacent properties
2.
The stationary sources are under common control
3.
The stationary sources belong to the same major industrial grouping (i.e., all activities have a Standard Industrial Classification (SIC) code beginning with the same two digits)
˃ Letter from William Wehrum (EPA) to Patrick
McDonnell (Pennsylvania DEP) re: Meadowbrook Energy LLC
Meadowbrook letter dated April 30, 2018
https://www.epa.gov/sites/production/files/2018-
05/documents/meadowbrook_2018.pdf
˃ Relevant for common control determinations
for co-located and support facilities
˃ Bottom Line:
Control assessment should focus on power of one entity to dictate air quality compliance decisions of other facility
Ability to “influence” does not constitute common control
Examples of air quality-related control include the power to:
♦Direct the construction/modification of emitting equipment ♦Dictate the manner in which these EUs operate ♦Make decisions re: the installation/operation of air pollution
control equipment
♦Direct monitoring, testing, recordkeeping, and reporting
If each entity has autonomy re: its AQ permitting
separate source
˃ Caveats:
Refining EPA’s interpretation and policy concerning
“common control” does not “change or substitute for any law, regulation, or other legally binding requirement”
♦ More fine print (in a footnote this time)!- This document is not a rule or regulation,
and the statements herein are not binding on state or local permitting authorities. This discussion reflects a change in how EPA interprets the term “common control” in it regulations but does not change or substitute for any law, regulation, or other legally binding requirement.
Local agencies may take more stringent
interpretation than federal guidance
Case-by-case assessment What if current permit documents same source
status?
˃ Reconsideration of 2009 project aggregation rule
Final reconsideration rule expected Summer 2018?
˃ Ambient air guidance
EPA evaluating potential for additional flexibility in
definitions of “general public”, “access”, “building”
Guidance expected soon
˃ Routine Maintenance, Repair and Replacement
(RMRR) guidance
EPA evaluating need for clarification of RMRR
interpretation and application
Clarification anticipated soon
Legal Developments and Updates
Session G
July 25, 2018
William H. Haak
Haak Law LLC
HAAK LAW LLC
Environmental, Health & Safety Legal and Consulting Services William H. Haak Tel: 216.772.3532 whh@haaklawllc.com
HAAK LAW LLC
Environmental, Health & Safety Legal and Consulting Services William H. Haak Tel: 216.772.3532 whh@haaklawllc.com
To Snatch Defeat From the Jaws of Victory...
USEPA must show actual emissions increase in order to commence enforcement
increase in actual emissions to enforce...Remands...
summary judgment for DTE again.
demand growth exclusion claim and emissions projections without need for actual increase in emissions
based on projections absent “clear error”
HAAK LAW LLC
Environmental, Health & Safety Legal and Consulting Services William H. Haak Tel: 216.772.3532 whh@haaklawllc.com
USEPA’s Changing NAAQS Approach
HAAK LAW LLC
Environmental, Health & Safety Legal and Consulting Services William H. Haak Tel: 216.772.3532 whh@haaklawllc.com
*P .S. Protect the environment and improve air quality...
The Legislative and Regulatory Future of the NAAQS
Costs and Benefits in the Rulemaking Process”
HAAK LAW LLC
Environmental, Health & Safety Legal and Consulting Services William H. Haak Tel: 216.772.3532 whh@haaklawllc.com
HAAK LAW LLC
Environmental, Health & Safety Legal and Consulting Services William H. Haak Tel: 216.772.3532 whh@haaklawllc.com