Title: New Source Review Reform Jim Little U'S' EPA Region 4 404 5629118 little'jamesepa'gov
1New Source Review Reform Jim LittleU.S. EPA
Region 4(404) 562-9118 little.james_at_epa.gov
- Air Waste Management Association, Mississippi
Chapter - 2005 Technical Conference
- Eagle Ridge Conference Center, Richmond,
Mississippi - November 8, 2005
2Outline
- New Source Review (NSR) Reform Background
- Status of State/Local NSR Rule Revisions
- Recent Court Actions on NSR
- Other Recent NSR Actions (Nonattainment Areas)
- Baseline Actual Emissions
- Actual-to-Projected-Actual Applicability Test
- Plantwide Applicability Limitation (PAL)
- Further Discussion
3Terminology
- Major NSR (for a specific geographic area)
- prevention of significant deterioration (PSD)
permitting for regulated NSR pollutants other
than nonattainment pollutants. - nonattainment area permitting for nonattainment
pollutants. - (Note Mississippi currently does not have any
nonattainment areas. All major NSR permitting in
Mississippi is therefore PSD permitting.)
4Terminology
- 2. EUSGU - electric utility steam generating
unit - 3. PTE - potential to emit used interchangeably
with allowable emissions in this presentation.
5Terminology
- 4. Regulated NSR Pollutant
- - National ambient air quality standard
pollutants (carbon monoxide, etc.) and EPA
designated precursors for such pollutants (e.g,
volatile organic compounds). - - Pollutants subject to a Clean Air Act section
111 standard (new source performance standards). - - Certain pollutants regulated by title VI of
the Clean Air Act (stratospheric ozone
protection). - - Other pollutants subject to regulation under
the Clean Air Act EXCEPT excludes section 112
hazardous air pollutants and pollutants regulated
by section 112(r) risk management plan
requirements (e.g., ammonia).
6NSR Reform Background December 2002 Rule
Revisions
- Issued December 31, 2002, and amended November 7,
2003. - Applies primarily to modifications of existing
sources. - Included five primary components
- baseline actual emissions definition
- actual-to-projected-actual applicability test
- plantwide applicability limitation (PAL)
- Clean Unit
- Pollution control project (PCP) exemption
7NSR Reform Background October 2003 Rule
Revisions
- Issued October 27, 2003.
- Referred to as Equipment Replacement Provision
(ERP) rules. - ERP rules specify when a replacement component
qualifies as a routine replacement and is
therefore exempt from NSR (i.e., is not a
physical change or change in the method of
operation). - Included 20-percent cost threshold test.
8NSR Reform Background October 2003 Rule
Revisions
- Stayed by U.S. Court of Appeals for the District
of Columbia Circuit (DC Circuit) on December 24,
2003. Remains stayed. - Should not be used by state and local reviewing
authorities as guidance to make routine
maintenance, repair, and replacement (RMRR)
determinations.
9Status of State/Local NSR Rule Revisions
- All of the 8 state and 10 local reviewing
authorities in Region 4 with NSR permitting
authority have SIP-approved programs (with one
small partial exception). Reviewing authorities
with SIP-approved programs have until January 2,
2006, to adopt NSR rule revisions and submit
proposed SIP changes to EPA. - Three Region 4 state reviewing authorities have
adopted revisions Mississippi, Kentucky, South
Carolina.
10Status of State/Local NSR Rule Revisions
- SIP gap the time from submittal of proposed
SIP changes until EPA approval. Theoretically,
permits issued under NSR rule revisions prior to
EPA approval of revisions into SIP could be
challenged. If state rules similar to (at least
as stringent as) federal rules, such challenges
not likely to prevail.
11Recent Court Actions on NSR - December 2002 NSR
Rule Revisions
- DC Circuit issued opinion on June 24, 2005.
- Vacated the Clean Unit and PCP exemption
components remanded one portion of the
actual-to-projected-actual component (related to
reasonable possibility).
12Recent Court Actions on NSR - December 2002 NSR
Rule Revisions
- EPA petitioned for rehearing on Clean Unit
component and asked for clarification on the PCP
exemption. Clarification sought is whether
vacating the PCP exemption will apply
prospectively only or will also require fixing
past PCP exemptions. - Because DC Circuit vacated Clean Unit and PCP
exemption components and because not included in
Mississippi rules, will not discuss these
components.
13Recent Court Actions on NSR Hourly Emissions
NSR Applicability Test
- U.S. Court of Appeals for the Fourth Circuit
issued opinion on June 15, 2005, that NSR
applicability for a modification should conform
to the new source performance standards (NSPS)
applicability test for a modification. NSPS
applicability test based on hourly emissions
whereas current NSR applicability test based on
annual emissions.
14Recent Court Actions on NSR Hourly Emissions
NSR Applicability Test
- Fourth Circuit decision directly affect only two
states in Region 4 North Carolina, South
Carolina. - EPA believes Fourth Circuit decision does not
affect state rules implemented pursuant to
December 2002 federal rule revisions because DC
Circuit upheld these revisions related to the use
of annual emissions. - EPA issued proposed rule on October 20, 2005,
proposing that NSR applicability test be changed
from an annual emissions basis to an hourly
emissions basis, but only for electric generating
units.
15Other Recent NSR Actions (Nonattainment Areas)
- No nonattainment areas in Mississippi.
- Proposed PM2.5 implementation rules, including
NSR, issued November 1, 2005. - Final 8-hour ozone implementation rules for NSR
expected soon.
16New NSR Applicability Test
- Baseline actual emissions
- Actual-to-projected-actual emissions
17- Understanding the New Applicability Test
- A project is a major modification for a regulated
NSR pollutant if it causes - A significant emissions increase on its own, and
- (2) A significant net emissions increase overall
18Understanding the New Applicability Test Old NSR
Requirements
- Non-EUSGUs Modified Units and New Emissions
Units Actual to Potential Test -
Compare past actual emissions to
future potential emissions. - Modified EUSGUs The WEPCO Test -
Compare past actual emissions to
representative actual annual emissions.
19Understanding the New Applicability Test New
Requirements
- Calculate projected actual emissions.
- Compare project actual emissions to baseline
actual emissions (actual-to-projected-actual
test). - New test can be used for replacement units also.
20Projected or Potential
- Use of projected actual emissions for comparison
with baseline actual emissions is optional. - Source owners can continue to use future
potential emissions compared with baseline actual
emissions to assess NSR applicability. This
approach has recordkeeping advantages (discussed
later).
21Baseline Actual Emissions
22Baseline Actual Emissions EUSGUs
- Similar to old WEPCO provisions.
- Baseline actual emissions are based on any
consecutive 24-month period within the 5 years
immediately preceding the project. - A baseline period prior to the last 5 years may
be used if the reviewing authority determines it
to be more representative of normal operations.
23Baseline Actual Emissions Non-EUSGUs
- Average annual emissions rate based on units
operation during any consecutive 24-month
period in the past 10 years. - Full 10-year look back acceptable if adequate
data accurately describing units operation are
available for the selected time period. - No other period may be used.
24Baseline Actual Emissions Non-EUSGUs
- For a single pollutant, use same 24-month period
for all emissions units involved in project. But
may use different 24-month period for each
pollutant. - Reduce for any non-compliant emissions, (those
that exceeded units allowable emission rate). - Adjust annual emissions rate for
non-operative portion of 24-month period.
25Adjustment to Baseline Calculation
- For existing emissions unit that did not exist
during the 24-month baseline period, count the
emissions rate as zero. - For existing emissions unit that operated for
portion of 24-month period, calculate average
rate using zero for that portion of time when
unit was not in operation.
26Adjustment to Baseline Calculation
- Adjust average annual rate to reflect current
emissions control requirements. An adjustment to
the baseline calculation is required if any
legally enforceable emissions limitation or
operating restriction (including but not limited
to a State or Federal requirement, such as RACT,
BACT, LAER, NSPS, NESHAP, etc.) currently applies
to the unit being changed. Not required for
EUSGUs.
27Adjustment to Baseline Calculation
- An adjustment should also be made for such things
as a more stringent fuel-use requirement (type or
amount of fuel), sulfur-in-fuel limit, etc. - Voluntary reductions resulting in enforceable
restrictions (e.g., use of clean fuel or
lower-polluting raw material to acquire
creditable reductions for netting) also must be
considered for adjustment of baseline.
28Adjustment to Baseline Calculation
- For a new unit (lt2 yrs old) that will be changed
by the project, baseline is - -- zero, if unit has not yet begun operation
- -- PTE, if the unit has begun operation.
29Baseline Actual EmissionsFugitive Emissions
Startup, Shutdown, and Malfunction Emissions
- Calculation of baseline actual emissions shall
include fugitive emissions to the extent
quantifiable. - Calculation of baseline actual emissions shall
include emissions associated with startups,
shutdowns, and malfunctions.
30Using Baseline Actual Emissions
- Baseline actual emissions used for
- Determining emissions increase resulting from
changes at existing units. - Computing contemporaneous emissions changes for
netting. - Establishing a PAL.
31Baseline Actual Emissions EXAMPLE 1
Year
VOC Emissions
1993
75 tpy
1994
85 tpy
New Rule Average annual emissions 90 tpy
1995
95 tpy
1996
80 tpy
Source did not have any more stringent emissions
limitations subsequently imposed thus, no
adjustment necessary.
1997
60 tpy
1998
80 tpy
1999
75 tpy
2000
40 tpy
2001
55 tpy
Old Rule Average annual emissions 65 tpy
2002
75 tpy
32Baseline Actual Emissions EXAMPLE 2
Year
VOC Emissions
1993
75 tpy
1994
50 tpy
1995
55 tpy
1996
60 tpy
1997
60 tpy
1998
65 tpy
1999
60 tpy
2000
40 tpy
2001
55 tpy
Old rule/ New rule Average annual emissions 65
tpy
2002
75 tpy
33Baseline Actual Emissions EXAMPLE 3
Year
VOC Emissions
1993
750 tpy
1994
850 tpy
New Rule Average annual emissions 900
tpy Adjusted baseline 900 x 0.10 90 tpy
1995
950 tpy
1996
800 tpy
Requirement for Thermal Oxidizer controls VOC
emissions by 90
1997
70 tpy
1998
60 tpy
1999
65 tpy
2000
60 tpy
2001
70 tpy
Old Rule Average annual emissions 68 tpy
2002
65 tpy
34Baseline Actual Emissions EXAMPLE 4
Year
VOC Emissions
1993
750 tpy
1994
850 tpy
Average annual emissions 900 tpy Adjusted
baseline 900 x 0.10 90 tpy
1995
950 tpy
1996
800 tpy
Requirement for Thermal Oxidizer controls VOC
emissions by 90
1997
60 tpy
1998
65 tpy
1999
85 tpy
2000
80 tpy
2001
90 tpy
New/Old Rule Avg. annual emissions 93 tpy
2002
95tpy
35Baseline Actual Emissions EXAMPLE 5 (EUSGU)
Year
SO2 Emissions
1998
150 tpy
1999
165 tpy
Old Rule Avg. annual emissions 170 tpy New
Rule Avg. annual emissions 170 tpy
2000
175 tpy
2001
150 tpy
2002
155 tpy
36Projected Actual Emissions
37Projected Actual Emissions Projection
Calculations
- Source owner must project changed units maximum
actual annual emissions for the 5-year
period after the change, - OR
- 10-year period after the change if the change
involves an increase in the emissions units PTE
or capacity.
38Projected Actual Emissions Projection
Calculations
- 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.
39Projected Actual Emissions Projection Calculations
- A units projected emissions rate is calculated
as the product of - (1) The hourly emissions rate -
- - Based on units post-change operational
capabilities - - Taking into account the legally enforceable
restrictions that could affect the hourly rate. - (2) The projected level of utilization, based on
- - Units historical annual utilization rate
- - Available information about units likely
post-change capacity utilization.
40Projected Actual Emissions Projection
Calculations
The applicant may adjust the projection to
exclude any portion of the emissions increase
that the changed unit -- could have
accommodated during the 24-month baseline
period, AND
-- is unrelated to the change. Includes
increased utilization due to demand growth.
41Projected Actual EmissionsFugitive Emissions
Startup, Shutdown, and Malfunction Emissions
- Calculation of projected actual emissions shall
include fugitive emissions to the extent
quantifiable. - Calculation of projected actual emissions shall
include emissions associated with startups,
shutdowns, and malfunctions.
42Notification, Recordkeeping, Reporting
43Recordkeeping and Reporting
- In Mississippi, all source owners are required to
keep records if they use the actual-to-projected-a
ctual test. - However, sources that show no significant
emissions increase by using units PTE rather
than projected actual emissions are not subject
to recordkeeping.
44Recordkeeping and Reporting
- Preconstruction notification for EUSGUs includes
- Project description
- Emissions units affected by project
- Description of applicability test used (baseline
emissions, projected emissions, amount of
excluded emissions and explanation). - Approval not needed to commence EUSGU project.
45Recordkeeping and Reporting
- Before beginning actual construction of a
project, source owner must document - description of project
- identification of emissions units whose emissions
of a regulated NSR pollutant could be affected by
project - description of the applicability test used to
determine that project is not a major
modification (baseline actual emissions,
projected actual emissions, could have
accommodated exclusions, netting calculations)
46Recordkeeping and Reporting
- For any modified unit, source must
- Monitor emissions of any regulated NSR pollutant
that could increase as a result of project - Calculate and maintain record of annual emissions
(tpy) for 5 (or 10) years following resumption
of units regular operation - If the project increases the design capacity or
PTE.
47Recordkeeping and Reporting
- Owners of EUSGUs must submit an annual report
within 60 days after end of each year listing
annual emissions during the calendar year that
preceded submission of the report.
48Recordkeeping and Reporting
- Owners of non-EUSGU modified units must submit a
report if annual emissions from project - Exceed the baseline actual emissions by
significant amount and - Differ from preconstruction projection.
-
- Is such reporting acknowledgment of a violation?
49Recordkeeping and Reporting
- For all modified emissions units, source owner
must make required information available for
review upon request by reviewing authority or
general public.
50Applicability Test EXAMPLE
Modification at Plant ABC Assumptions Existing
Major Source, Attainment Area, VOC Emissions
Plant ABC began operations in late 2000
Year
VOC Actual Emissions
Post-change Potential Emissions 300 tpy VOC
2001
125 tpy
2002
135 tpy
2003
155 tpy (projected)
2004
155 tpy (projected)
2005
160 tpy (projected)
2006
160 tpy (projected)
2007
165 tpy (projected)
51Applicability Test (Old Rule) EXAMPLE
Modification at Plant ABC Assumptions Existing
Major Source, Attainment Area, VOC Emissions
Plant ABC began operations in late 2000
Future Potential Emissions 300 tpy VOC
Year
VOC Actual Emissions
2001
125 tpy
2002
135 tpy
2003
155 tpy (projected)
Old Rule past actual (130 tpy) vs. future PTE
(300 tpy) Proposed Increase 170 tpy gt40
tpy Net emissions increase 170 tpygt40 tpy
Modification subject to PSD
2004
155 tpy (projected)
2005
160 tpy (projected)
2006
160 tpy (projected)
2007
165 tpy (projected)
52Applicability Test (New Rule) EXAMPLE
Modification at Plant ABC Assumptions Existing
Major Source, Attainment Area, VOC Emissions
Plant ABC began operations in late 2000
Year
VOC Actual Emissions
Future Potential Emissions 300 tpy VOC
2001
125 tpy
2002
135 tpy
New Rule Baseline actual emissions (130 tpy) vs.
projected actual (165 tpy) Projected Increase
35 tpy lt 40 tpy MINOR MODIFICATION
2003
155 tpy (projected)
2004
155 tpy (projected)
2005
160 tpy (projected)
2006
160 tpy (projected)
2007
165 tpy (projected)
53Plantwide Applicability Limitations (PALs)
54Plantwide Applicability Limitations
- An alternative approach for determining major NSR
applicability. -
- The new rules address only actuals PALs. EPA
may consider provisions for allowables PALs at
a later date.
55Plantwide Applicability Limitations
- A PAL is an annual (facility-wide) emission
limitation (12-month total, rolled monthly) under
which the facility can make any changes without
triggering NSR review for that pollutant. - Pollutant-specific
- 10-year term.
- Can be used in nonattainment areas.
- A separate PAL permit is required for each
pollutant.
56Establishing a PAL
- At the time of setting a PAL, classify all
emissions units as new or existing. - Determine baseline actual emissions of all units
- For new units, add the PTE of the units
- For existing units, calculate baseline actual
emissions as previously described, except - For existing units constructed after the baseline
period, add the PTE of the units.
57Establishing a PAL
- Add the pollutant-specific significant emissions
rate to the emissions calculated as described
above - Subtract any emissions from emissions units that
operated during the 24-month period and have
since been permanently shut down and - Establish a step-down PAL if there are any
requirements that have an effective date during
the term of the PAL.
58Reopening PAL Permits
- Reviewing authority shall reopen the PAL permit
to - Correct typographical or calculation errors made
in setting the PAL. - Reduce the PAL to create emissions reductions for
offset purposes. - Revise the PAL to reflect an increase in the PAL.
59Reopening PAL Permits
- Reviewing authority may reopen the PAL permit to
- Reduce the PAL to reflect newly applicable
federal requirements with compliance dates after
the PAL effective date. (However, PAL must be
adjusted at title V or PAL permit renewal,
whichever occurs first.) - Reduce the PAL consistent with any other
requirement that the reviewing authority may
impose under its SIP. - Reduce the PAL if it determines that a reduction
is necessary to avoid causing or contributing to
a NAAQS or PSD increment violation.
60Increasing a PAL
- Allowed if increased emissions can not be
accommodated under the PAL, even if all
significant and major emissions units were to
meet a BACT level of control. - Emissions units causing the need for an increase
(modified or new units) must go through major
NSR. - New PAL based on sum of
- Baseline actual emissions of small emissions
units - Baseline actual emissions of significant and
major emissions units assuming a BACT level of
control and, - Allowable emissions of new or modified emissions
units.
61PAL Renewal
- At least 6 months prior to but not earlier than
18 months from PAL expiration date, the owner
must submit an application for renewal or
expiration. - The reviewing authority shall provide a written
rationale for the proposed PAL level for public
comment. - The new PAL level can not be higher than the
existing PAL (unless PAL increase provisions are
met) or the PTE of the source.
62PAL Renewal
- If baseline actual emissions plus significant
level are 80 of current PAL, then PAL may be
renewed at current level. - If baseline actual emissions plus significant
level are lt 80 then - PAL may be established at a level that is more
representative of baseline actual emissions, or a
level that is appropriate based on air quality
needs or other considerations.
63PAL Expiration
- Within the timeframe specified for PAL renewals,
the source shall submit a proposed allocation of
the PAL to each emissions unit. - The reviewing authority shall decide whether and
how the PAL will be distributed and issue a
revised permit incorporating allowable limits for
each emissions unit. - Any subsequent physical or operational change at
the source will be subject to major NSR review.
64PAL Monitoring Requirements
- PAL permit must contain enforceable requirements
to determine plantwide emissions (12-month
total, rolled monthly). - A source may use any of the following approaches
- Mass balance calculations for activities using
solvents or coatings. - Continuous Emissions Monitoring Systems (CEMS).
- Continuous Parameter Monitoring Systems (CPMS) or
Predictive Emissions Monitoring Systems (PEMS). - Emissions Factors.
65PAL Monitoring Requirements
- If no monitoring data exist for an emissions unit
for a time period, the source owner must report
the maximum potential emissions without
considering enforceable or operating emissions
limitations, unless another method is specified
in the permit.
66PAL Monitoring
- Where an owner cannot demonstrate a correlation
between the monitored parameter(s) and the PAL
pollutant emissions rate at all operating points
of an emissions unit, the reviewing authority
shall at the time of permit issuance - Establish default value(s) for determining
compliance with the PAL based on the highest
potential emissions reasonably estimated at such
operating points or - Determine that the operation of the emissions
unit in the absence of a correlation is a
violation of the PAL.
67Recordkeeping/Reporting
- The PAL permit shall require the owner to
maintain the following records for the duration
of the PAL effective period plus 5 years - A copy of the PAL permit application and any
applications for revisions to the PAL and - Each annual certification of compliance pursuant
to title V and the data relied on in certifying
the compliance. - The owner shall submit semi-annual monitoring
reports and prompt deviation reports to the
reviewing authority in accordance with the
applicable title V permitting program.
68PAL EXAMPLE
3 units 50 tpy actual VOC emissions each during
baseline period. 1 unit shutdown since then.
Hence PAL level 150 40 -50 140 tpy. Any
change not subject to major NSR if plantwide
emissions remain below 140 tpy VOC. 40 tpy is
significant emissions rate for VOC
69Questions?