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Title: New Source Review Reform Jim Little U'S' EPA Region 4 404 5629118 little'jamesepa'gov


1
New 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

2
Outline
  • 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

3
Terminology
  • 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.)

4
Terminology
  • 2. EUSGU - electric utility steam generating
    unit
  • 3. PTE - potential to emit used interchangeably
    with allowable emissions in this presentation.

5
Terminology
  • 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).

6
NSR 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

7
NSR 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.

8
NSR 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.

9
Status 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.

10
Status 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.

11
Recent 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).

12
Recent 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.

13
Recent 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.

14
Recent 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.

15
Other 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.

16
New 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

18
Understanding 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.

19
Understanding 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.

20
Projected 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).

21
Baseline Actual Emissions
22
Baseline 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.

23
Baseline 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.

24
Baseline 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.

25
Adjustment 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.

26
Adjustment 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.

27
Adjustment 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.

28
Adjustment 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.

29
Baseline 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.

30
Using 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.

31
Baseline 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
32
Baseline 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
33
Baseline 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
34
Baseline 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
35
Baseline 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
36
Projected Actual Emissions
37
Projected 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.

38
Projected 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.

39
Projected 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.

40
Projected 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.
41
Projected 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.

42
Notification, Recordkeeping, Reporting
43
Recordkeeping 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.

44
Recordkeeping 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.

45
Recordkeeping 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)

46
Recordkeeping 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.

47
Recordkeeping 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.

48
Recordkeeping 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?

49
Recordkeeping and Reporting
  • For all modified emissions units, source owner
    must make required information available for
    review upon request by reviewing authority or
    general public.

50
Applicability 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)
51
Applicability 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)
52
Applicability 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)
53
Plantwide Applicability Limitations (PALs)
54
Plantwide 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.

55
Plantwide 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.

56
Establishing 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.

57
Establishing 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.

58
Reopening 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.

59
Reopening 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.

60
Increasing 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.

61
PAL 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.

62
PAL 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.

63
PAL 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.

64
PAL 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.

65
PAL 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.

66
PAL 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.

67
Recordkeeping/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.

68
PAL 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
69
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