Revisions to the Guideline on Air Quality Models

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Revisions to the Guideline on Air Quality Models (GAQM)

Revisions to the Guideline on Air Quality Models (GAQM)

Guideline on Air Quality Models What is it? Why have it? • EPA-preferred models

Guideline on Air Quality Models What is it? Why have it? • EPA-preferred models • Recommended techniques • Common basis and consistency • App. W to 40 CFR Part 51 Where is it?

Timeline January 17, 2017 Promulgated revisions to the Guideline May 22, 2017 Effective date

Timeline January 17, 2017 Promulgated revisions to the Guideline May 22, 2017 Effective date May 22, 2018 End of transition period

Updates: AERMOD Modeling System q New Version q AERMOD 16216 r q Horizontal/capped stack

Updates: AERMOD Modeling System q New Version q AERMOD 16216 r q Horizontal/capped stack q BLP q NO 2 Tier 2 & 3 q AERMET 16216 q ADJ_U* q Other enhancements/bug fixes

Updates: 3 -Tiered Approach for NO 2 Tier 1: 100 % conversion (no change)

Updates: 3 -Tiered Approach for NO 2 Tier 1: 100 % conversion (no change) Tier 2: Ambient equilibrium NO: NO 2 (ARM to ARM 2) Tier 3: NOx: NO 2 through ozone titration (PVMRM & OLM)

Updates: 3 -Tiered Approach for NO 2 Based on hourly data of NO 2:

Updates: 3 -Tiered Approach for NO 2 Based on hourly data of NO 2: NOx, q Based on hourly data of NO 2: NO Empirically derived equation in x ratios min ratio: 0. 5 & max ratio: AERMOD, 0. 9 equation in q Empirically derived AERMOD q Min ratio: 0. 5 & Max ratio: 0. 9

Updates: 3 -Tiered Approach for NO 2 Tier 3: PVMRM & OLM q Regulatory

Updates: 3 -Tiered Approach for NO 2 Tier 3: PVMRM & OLM q Regulatory default version of AERMOD, AERMOD Revised PVMRM, still need to with us on model inputs qcoordinate Revised PVMRM q ADMT coordination on model inputs

Revisions: Meteorological Input AERMINUT E: 1 -min ASOS wind data Reduces calm & missing

Revisions: Meteorological Input AERMINUT E: 1 -min ASOS wind data Reduces calm & missing hours Included in TCEQ processing

Revisions: Meteorological Input AERMINUTE: Processor: 1 -min ASOS wind data Reduces calm & missing

Revisions: Meteorological Input AERMINUTE: Processor: 1 -min ASOS wind data Reduces calm & missing hours Included in TCEQ processing

Revisions: Meteorological Input AERMINUTE: 1 -min ASOS wind data Reduces calm & missing hours

Revisions: Meteorological Input AERMINUTE: 1 -min ASOS wind data Reduces calm & missing hours Included in TCEQ processing

Revisions: Meteorological Input AERMINUTE: 1 -min ASOS wind data Reduces calm & missing hours

Revisions: Meteorological Input AERMINUTE: 1 -min ASOS wind data Reduces calm & missing hours Included in TCEQ processing

AERSCREEN Status of AERSCREEN Preferred screening model Version 16216 ADJ_U*

AERSCREEN Status of AERSCREEN Preferred screening model Version 16216 ADJ_U*

Single Source Impacts on O 3 & Secondary PM 2. 5 EPA is recommending

Single Source Impacts on O 3 & Secondary PM 2. 5 EPA is recommending two-tier approach: Tier 1: relationship precursor emissions source impact Tier 2: photochemical grid modeling

Single Source Impacts on O 3 & Secondary PM 2. 5 Tier 1: relationship

Single Source Impacts on O 3 & Secondary PM 2. 5 Tier 1: relationship precursor emissions – source impact q. Peer-reviewed –reviewed literature, q. Previous modeling results (MERPs), Reduced-form model (MERPs) q Reduced-form model

Single Source Impacts on O 3 & Secondary PM 2. 5 Tier 2: photochemical

Single Source Impacts on O 3 & Secondary PM 2. 5 Tier 2: photochemical grid modeling New draft guidance, consult with q New draft guidance us early q Consult with ADMT early

Modeled Emission Rates for Precursors (MERPs) Represents a level of emissions of precursors that

Modeled Emission Rates for Precursors (MERPs) Represents a level of emissions of precursors that is not expected to contribute significantly to concentrations of ozone or secondarily-formed PM 2. 5

Modeled Emission Rates for Precursors (MERPs) MERP (tpy) = Critical Air Quality Threshold (µg/m

Modeled Emission Rates for Precursors (MERPs) MERP (tpy) = Critical Air Quality Threshold (µg/m 3 or ppb) Modeled emission rate from hypothetical source (tpy) Modeled air quality impact from hypothetical source (µg/m 3 or ppb)

Modeled Emission Rates for Precursors (MERPs) Precursor NOx NOx SO 2 SO 3 SO

Modeled Emission Rates for Precursors (MERPs) Precursor NOx NOx SO 2 SO 3 SO 4 VOC VOC Region Central US Eastern US Western US 8 -hr O 3 126 170 184 ---948 1, 159 1, 049 Daily PM 2. 5 1, 693 2, 295 1, 075 238 628 210 ---- Annual PM 2. 5 5, 496 10, 144 3, 184 839 4, 013 2, 289 ----

Using a MERP • Precursor emissions must be < MERP value 1 Precursor

Using a MERP • Precursor emissions must be < MERP value 1 Precursor

Using a MERP • Both precursors’ emissions must be < MERP value • Additive

Using a MERP • Both precursors’ emissions must be < MERP value • Additive impacts analysis • PM 2. 5 must also consider primary impact 2 Precursors

Example o Facility with proposed increase of 35 tpy of primary PM 2. 5

Example o Facility with proposed increase of 35 tpy of primary PM 2. 5 o 110 tpy of NOx o 75 tpy of SO 2 o Located in the Central U. S.

O 3 Analysis NOX emissions of 110 tpy are lower than the NOX MERP

O 3 Analysis NOX emissions of 110 tpy are lower than the NOX MERP for 8 -hr O 3 in the central region of the U. S. Precursor NOx NOx SO 2 SO 3 SO 4 VOC VOC Region Central US Eastern US Western US 8 -hr O 3 126 170 184 ---948 1, 159 1, 049 Daily PM 2. 5 1, 693 2, 295 1, 075 238 628 210 ---- Annual PM 2. 5 5, 496 10, 144 3, 184 839 4, 013 2, 289 ----

PM 2. 5 Analysis NOX and SO 2 emissions are below the lowest daily

PM 2. 5 Analysis NOX and SO 2 emissions are below the lowest daily and annual PM 2. 5 MERP values of any source modeled in the Central U. S. Precursor NOx NOx SO 2 SO 3 SO 4 VOC VOC Region Central US Eastern US Western US 8 -hr O 3 126 170 184 ---948 1, 159 1, 049 Daily PM 2. 5 1, 693 2, 295 1, 075 238 628 210 ---- Annual PM 2. 5 5, 496 10, 144 3, 184 839 4, 013 2, 289 ----

PM 2. 5 Analysis: Additive Secondary Impacts on Daily PM 2. 5 (110 tpy

PM 2. 5 Analysis: Additive Secondary Impacts on Daily PM 2. 5 (110 tpy NOX from source / 1, 693 tpy NOX daily PM 2. 5 MERP) + (75 tpy SO 2 from source / 238 tpy SO 2 daily PM 2. 5 MERP) =. 06 +. 32 =. 38 * 100 = 38%

PM 2. 5 Analysis: Additive Secondary Impacts on Annual PM 2. 5 (110 tpy

PM 2. 5 Analysis: Additive Secondary Impacts on Annual PM 2. 5 (110 tpy NOX from source / 5, 496 tpy NOX annual PM 2. 5 MERP) + (75 tpy SO 2 from source / 839 tpy SO 2 annual PM 2. 5 MERP) =. 02 +. 09 =. 11 * 100 = 11%

PM 2. 5 Analysis: Primary + Secondary Primary 24 -hr PM 2. 5 impact

PM 2. 5 Analysis: Primary + Secondary Primary 24 -hr PM 2. 5 impact from AERMOD = 0. 45 µg/m 3 Primary impact is 35% of the critical air quality threshold: 0. 45 µg/m 3 / 1. 2 µg/m 3 = 35% Primary impact (35%) + secondary impacts (38%) = 73% and <100%

Modeled Emission Rates for Precursors (MERPs) • Lowest derived MERPs on a national level

Modeled Emission Rates for Precursors (MERPs) • Lowest derived MERPs on a national level 1 • Lowest derived MERPs only for Texas sources 2 • MERPs derived for a specific Texas source 3

Updates: Cumulative Impact Analysis Modeling Dom Domain: Geographic area for analysis extending: Includes area

Updates: Cumulative Impact Analysis Modeling Dom Domain: Geographic area for analysis extending: Includes area extending: q distant significant impact • distant significant qimpact or 50 km, whichever is less • 50 kilometers, whichever is less

Updates: Cumulative Impact Analysis New/Modified q New/modified source: emissions allowable Emiss emissions Emissions Nearbysource:

Updates: Cumulative Impact Analysis New/Modified q New/modified source: emissions allowable Emiss emissions Emissions Nearbysource: actual • q. Nearby Input Data: emissions data actual emissions Data: data q Other source: represented • Other source: by monitoring data represented by monitoring data

Updates: Cumulative Impact Analysis Nearby source: Other source: • in vicinity of source under

Updates: Cumulative Impact Analysis Nearby source: Other source: • in vicinity of source under consideration: • explicitly model • all other sources: • accounted for by monitoring data

Updates: Cumulative Impact Analysis Determining appropriate background concentrations Isolated source Multi-source area

Updates: Cumulative Impact Analysis Determining appropriate background concentrations Isolated source Multi-source area

Updates: Cumulative Impact Analysis Isolated: focus on other sources through ambient monitoring data

Updates: Cumulative Impact Analysis Isolated: focus on other sources through ambient monitoring data

Updates: Cumulative Impact Analysis Multi-source: determine nearby sources & ambient monitoring data for other

Updates: Cumulative Impact Analysis Multi-source: determine nearby sources & ambient monitoring data for other sources

Thank You! • Amanda Jones (512) 239 -1229 Amanda. Jones@tceq. texas. gov • Rachel

Thank You! • Amanda Jones (512) 239 -1229 Amanda. Jones@tceq. texas. gov • Rachel Melton (512) 239 -2358 Rachel. Melton@tceq. texas. gov • Dianne Anderson Team Leader – Air Dispersion Modeling Team (512) 239 -5761 Dianne. Anderson@tceq. texas. gov