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October 30, 2013 – AWMA Fall Conference
Session 3 – Hot Air Topics
Presented by
Michael Carbon
Practical Applications for
Applying PSD Actual-to-
Projected Actual Analysis
Overview of Presentation
1. Very brief overview of New Source Review (NSR)
2. Review applicability options post-2002 NSR Reform
3. Review the steps required to perform a NSR
applicability analysis with emphasis on the baseline
actual-to-projected actual emissions analysis including
practical examples and relevant EPA policy
determinations
What is NSR?
• NSR is a preconstruction permitting program
designed to support NAAQS attainment and
maintenance
• NSR permitting is required for – New major sources
– Major modifications at existing major sources
• NSR is comprised of two separate programs– Prevention of Significant Deterioration (PSD) - PSD applies in
attainment areas
– Nonattainment New Source Review (NNSR) - NNSR applies in
nonattainment areas
Post‐2002 NSR Reform Applicability Tests
Baseline Actual Emissions‐to‐PTE (A2P)
• Required for new emissions units and can also be used for existing
emissions units
• Project-Only Emissions Change = Potential Emissions – Baseline Actual
Emissions
Baseline Actual Emissions‐to‐Projected Actual Emissions (A2PA)
• Can only be used for existing emissions units (including replacement
units)
• Project-Only Emissions Change = (Projected Actual Emissions – Baseline
Actual Emissions) – Excluded But Could Have Been Accommodated
Emissions
*For today’s presentation, we will focus on the applicability criteria for non-EUSGUs
NSR Applicability Options
Steps of NSR Applicability Analysis
1. Define your project, determine the project-affected emissions units, and categorize project-affected emissions units (new, existing, or replacement)
2. Determine the baseline actual emissions (BAE) for each affected emissions unit
3. Determine the projected actual emissions (PAE) or potential to emit (PTE) for each affected emissions unit
4. Determine the project emissions increases only for each pollutant
5. Determine contemporaneous increases and decreases for any pollutant with significant project emissions increase
6. Determine net emissions increase for each pollutant subject to netting
Step 1a: Define the Project
• Define scope of the Project….
– Could include multiple capital projects in multiple process units
occurring over several years
– When performing an NSR aggregation analysis for multiple projects
you should consider whether the projects are economically or
technically linked following EPA’s 3M-Maplewood memo guidance
and the more recently stayed NSR aggregation amendments
Step 1b: Determine Project-Affected
Emissions Units
• What is an emissions unit?
– “Emissions unit” is any part of a major stationary source which emits
or would have the potential to emit any regulated pollutant
– Heaters, boilers, tanks, flares, fugitive components, etc.
• What is a project-affected emissions unit?
– Any new emissions unit installed as part of the project
– Any emissions unit physically modified as part of the project
– Any emissions unit that experiences the following due to the project:
an increase in feed or production, a change in fuel or raw material, a
shift to higher emitting yield….
Step 1c: Categorize Project-Affected
Emissions Units
• New emissions unit
– Is, or will be, newly constructed and has existed for less than two
years from the date the unit first operated
• Existing emissions unit
– Not a new emissions unit
– Replacement unit is an existing emissions unit
• Replacement unit
– Reconstructed per NSPS or “completely takes the place”
– Identical to or functionally equivalent
– Does not alter basic design parameters of the process unit
– Replaced unit is permanently removed, disabled or barred from
operation by permit
Step 2: Baseline Actual Emissions
• Determine baseline actual emissions (BAE) for each project-
affected emissions unit
• Definition of BAE depends on the type of emissions unit
– New emissions units, proposed with this project
– New emissions units, proposed with a different project
– Existing emissions units
– Replacement units
Step 2a: Baseline Actual Emissions for
New Emissions Units
• For new emissions units proposed to be constructed
with the project
– Baseline actual emissions equal zero
• For new emissions units affected by the project (i.e.,
emissions units that have existed for less than two years
since first operated)
– Baseline actual emissions equals the PTE
– Avoids redundant review for new emissions units that were part
of another project
Step 2a: Baseline Actual Emissions for
New Emissions Units (cont’d)That sounded easy…..or did it. What if an emissions unit has
operated less than two years at the time a permit application is
submitted but by the time start of construction of the project
occurs the unit will have operated for at least two years?
– Would state/EPA expect the emissions unit to be treated as a
new or existing emissions unit?
• If you treat it as an existing emissions unit, then the baseline actual
emissions would have to be based on less than 24 months of actual
emissions data….
• Alternatively, if it were treated as a new emissions unit (PTE-to-
PTE) in the application, would there be an obligation to revisit the
applicability analysis after the unit has operated for 24 months if that
occurs prior to construction or start-up?
– To date, no applicability determinations have addressed this
specific issue
Step 2b: Baseline Actual Emissions –
Existing Units
• The average rate of actual emissions, in tons per year
• During any consecutive 24 months
• Within the 10-year period immediately preceding
– either the date the owner or operator begins actual construction of the project
– or the date a complete permit application is received by LDEQ
• For a given pollutant, the same baseline period must be used for all affected emissions units
– A different baseline period may be selected for each pollutant
Step 2b: Baseline Actual Emissions –
Existing Units (cont’d)
• Include fugitive emissions
• Include authorized emissions associated with Startups,
Shutdowns and Malfunctions
• Adjust downward to exclude any non-compliant emissions that
occurred while the source was operating above any emission
limitation that was legally enforceable during the consecutive
24-month period
• Adjusted downward to exclude emissions that would have
exceeded an emission limitation with which the source must
currently comply, had such source been required to comply
with such limitations during the consecutive 24-month period
Step 2b: Baseline Actual Emissions –
Existing Units (cont’d)
Some considerations when picking your baseline period:
– Must have adequate information and data quality to make the
required adjustments
– Older time periods typically require more adjustments
– May need to revise emissions using new factors (make sure you’re
not comparing apples to oranges….or you get mixed fruit)
– May not have enough information to evaluate compliance with limits
that didn’t apply at the time
– More recent time periods generally have more reliable, better quality
emissions data
– For first pass review, typically use most recent two years’ data
Step 2c: Baseline Actual Emissions –
Replacement Units
• Replacement units, by definition, are considered to be
existing units
• Baseline period emissions of the unit being replaced are
used to establish BAE
Step 3: Projected Actual Emissions (PAE) or
Potential to Emit (PTE)
Determine post-project emissions for each project affected
emissions unit
• Calculation of post-project emissions depends on the type of
emissions unit
– New emissions units
• Must use Potential to Emit
– Existing emissions units, including replacement units
• Can use Projected Actual Emissions or Potential to Emit
• Option to use PTE to represent post-project emissions
– PTE is always the most conservative
– PTE is easy
– Use PTE as the first pass in project reviews
Step 3a: Post-Project Emissions –
New Units
• For new units being proposed with the project
– Post-project emissions equal PTE
• Potential to emit is the maximum capacity of a stationary source to
emit a pollutant under its physical and operational design
• For new units affected by the project (i.e. less than two
years since first operated)
– Post-project emissions equal PTE
• As discussed previously, BAE also equal to PTE so project increase
is always zero
• Avoids redundant review for new units that were part of another
project
Step 3b: Post-Project Emissions - Existing
Units• For existing emissions unit, select either
– Projected actual emissions or potential to emit
• Projected actual emissions for non EUSGU is – the max annual rate, in tpy, at which an existing emissions unit is projected
to emit a regulated pollutant – in any one of the five years (12-month period) following the date the unit
resumes regular operation after the project– or in any one of the 10 years following that date,
- if the project involves increasing the emissions unit’s design capacity or- if its potential to emit would result in a significant emissions increase or
a significant net emissions increase at the source.
• Projected actual emissions - The first year begins on the day the emissions unit resumes regular operation following the change and includes the 12 months after this date. So not always consistent with calendar year emissions.
Step 3b: Post-Project Emissions -
Existing Units (cont’d)
Projected Actual Emissions must• Include fugitive emissions
• Include authorized emissions associated with startups,
shutdowns, and malfunctions
• Consider all “relevant information”
– Historical operation
– Company representations, filings with authorities
– Highest projections of expected business activity
Step 3b: Post-Project Emissions -
Existing Units (cont’d)Projected Actual Emissions may
• Exclude, in calculating any increase in emissions that
results from the particular project,
– emissions the existing unit could have accommodated during the
baseline period and
– that are also unrelated to the particular project
– including any increased utilization due to product demand growth
• This is called the Demand Growth Exclusion
– The intent of the NSR Reform rule is to limit PSD applicability to
consideration of emissions that will result from the project
Step 3b: Post-Project Emissions -
Existing Units (cont’d)
So what guidance is out there regarding PAE emissions:
– April 20, 2010 Region 3 letter to Pennsylvania Department of
Environmental Protection regarding the Northampton Generating
Company PSD/NSR Analysis
• “EPA has observed that a common mistake is to assume that a unit “could” have
emitted up to its permitted amount during the baseline period and this is the
amount that can be excluded from the PAE. This notion and any variation of this
notion is incorrect.”
• “…facility can only subtract that portion of the projected actual emissions that the
unit(s) could have already physically and legally emitted during the baseline
year. For instance, a facility is permitted to burn coal with a sulfur content up to
two percent but actually burns coal with one percent sulfur during the baseline
period. The company bases the projected actual emissions on continuing to
burn one percent sulfur coal. Emissions that can be excluded would be limited
to emissions associated with burning one percent coal, regardless of the limit
that would allow them to burn a higher sulfur coal.”
Step 3b: Post-Project Emissions -
Existing Units (cont’d)
– March 18, 2010 Region 4 letter to Georgia-Pacific Wood
Products LLC
• “We acknowledge that Georgia Pacific may use the highest
demonstrated average monthly operating level during the baseline
period as an approximation of the level of operation that the units
“could have accommodated” during the baseline period.”
– Note that if the facility cannot achieve the demonstrated average monthly
operating level for a sustained period (2 years) of time due to process
limitations……it can’t justify that it is capable of accommodating up to that
rate.
Step 3b: Post-Project Emissions -
Existing Units (cont’d)
Common examples of emissions excluded from
PAE• Low market demand during the baseline period
• Natural disasters (Hurricanes, floods, power outages) that occurred
during baseline period
• Non project related upsets due to equipment failures that occurred
during the baseline period if the particular failure is not routine
• Products/materials at a loading rack that are not impacted by the
project
• Process vents routed to a flare or thermal oxidizer that are not
impacted by the project
Step 4 – Determine Project Emissions
Increases
• Calculate the difference between PAE or PTE (Step 3) and BAE
(Step 2) for each emissions unit
• Sum only the increases for each emissions unit
- Decreases are not counted at this step
- There can be no negative numbers! If a unit’s post change emissions are
lower than the baseline actual emissions, the increase is zero, i.e. there is
no actual emissions increase.
- Creditable decreases can be taken in netting, if applicable
• Compare the project-related emissions increases to the PSD
Significance Levels for each pollutant to determine if the project
results in a significant emissions increase for any NSR-
regulated pollutant.
Step 5 – Determine Contemporaneous
Emission Increases
• If Step 4 results in a significant emissions
increase for a regulated pollutant
– Determine all creditable contemporaneous increases
and decreases for that pollutant
– Actual-to-potential test is the only test allowed for
contemporaneous increases and decreases• Per Federal Register/Vol. 67, No. 251/Tuesday, December 31, 2002/Rules
and Regulations 80203; and April 4, 2011 Region 5 letter to Indiana
Department of Environmental Management
• Sum project increases and creditable contemporaneous
emission increases and decreases
• If above significance threshold NSR review is applicable
Step 6 – Determine Net Emissions
Increase
Don’t forget the applicable “reasonable
possibility” pre-change recordkeeping, post-
change recordkeeping (including emissions
monitoring), and reporting requirements.
Remember…….