Implementation Issues for the 2006 24-Hour PM2.5 Standard EPA / WESTAR Residential Wood Smoke Workshop Salt Lake City, Utah March 1, 2011 Rich Damberg.

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Presentation transcript:

Implementation Issues for the Hour PM2.5 Standard EPA / WESTAR Residential Wood Smoke Workshop Salt Lake City, Utah March 1, 2011 Rich Damberg EPA Office of Air Quality Planning and Standards Salt Lake City, 2/3/09

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3 Overview PM2.5 standards and nonattainment areas Implementation timelines Attaining the Hour PM2.5 standard PM2.5 implementation rule requirements Strategies for Reducing Residential Wood Smoke (EPA guidance, October 2009) Black carbon and climate

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5 PM NAAQS 1987 / 1997 Standards2006 Standards Annual24-hourAnnual24-hour PM 2.5 (Fine Particles) 15 µg/m 3 Annual arithmetic mean, averaged over 3 years (established in 1997) 65 µg/m hour average, 98 th percentile, averaged over 3 years (estab. In 1997) 15 µg/m 3 Annual arithmetic mean, averaged over 3 years 35 µg/m hour average, 98 th percentile, averaged over 3 years PM 10 (Coarse Particles) 50 µg/m 3 Annual average (established in 1987) 150 µg/m 3 24-hr average, not to be exceeded more than once per year on avg. over a 3-yr period Revoked150 µg/m 3 24-hr average, not to be exceeded more than once per year on avg. over a 3-yr period Health effects are significant Aggravated asthma Increases in respiratory symptoms like coughing, painful breathing Chronic bronchitis Decreased lung function Premature death in people with heart and lung disease

PM 2.5 NAAQS 1997 PM 2.5 NAAQS –Estimated benefits = $43-97 billion; estimated costs = $6.7 billion –39 nonattainment areas designated in 2005 (with 88 million population) –State plans were due in 2008 –28 of 39 areas are attaining based on data –SO2 reductions from power industry were key strategy 2006 PM 2.5 NAAQS –Estimated benefits = $17 billion; estimated costs = $5.4 billion –31 nonattainment areas designated in 2009 (with 70 million population); state plans are due in December 2012 –Several new western areas with high winter values –Larger role for nitrate and carbonaceous PM 2.5 (e.g., wood smoke) –Transport Rule to provide continued SO2 reductions in Eastern U.S. –Primary annual and secondary standards were remanded to EPA 6

PM2.5 Nonattainment Areas Designated in 2005 and 2009

Timeline for PM2.5 NAAQS Implementation Milestone1997 PM2.5 NAAQS2006 PM2.5 NAAQS Effective Date of Standard September 1997December 2006 Effective Date of Designations April 2005December 2009 SIPs DueApril 2008December 2012 Attainment DateApril 2010 (based on monitoring data) Early 2015 (based on monitoring data) Attainment Date with Extension Up to April 2015Up to early 2020 (based on monitoring data)

9 Attaining the Hour PM2.5 Standard Significant health benefits will be achieved through state and local actions to attain the standard! Regulatory impact analysis for 2006 PM NAAQS –Provides example control strategies and modeling –Direct PM2.5 emission reductions provide greatest air quality improvement and health benefits per ton – Not planning to issue new implementation rule at this time Framework of existing implementation rule is appropriate for attainment planning for 2006 PM2.5 standards

10 PM2.5 Implementation Rule PM2.5 implementation rule (2007) –Precursor policies –Emission inventory –Control measures –Attainment demonstration Control measures (RACM / RACT) Modeling and other analyses Attainment date – “as expeditiously as practicable” –Reasonable further progress –Contingency measures –Enforceable regulations June 2007 workshop presentations provide detailed information on implementation rule issues. –See

11 State Implementation Plans for 24-Hour PM2.5 Standard Develop baseline and projection year emission inventories –Baseline inventory: most recent statewide inventory, “or other suitable year” –Can use seasonal inventory if all exceedances occur in same season(s) Account for projected reductions and air quality improvement from Federal and State rules on the books Evaluate controls for local and in-state contributors to the nonattainment problem Adopt rules for reasonably available measures (RACM/RACT) for area to attain “as expeditiously as practicable” Presumption: attain within five years (early 2015 based on data) –If cannot show area will attain in 5 years, request for attainment date up to 10 years is possible as part of SIP submittal RFP plan needed if have attainment date exceeding five years

12 Pollutants to Address in Attainment Plans Direct PM2.5 and SO2: must be evaluated for control measures in each area NOx: Sources of NOx must be evaluated for control measures in each area, unless the State and EPA provide a technical demonstration showing that NOx emissions from sources in the State do not significantly contribute to PM2.5 concentrations in a specific area VOC and ammonia: Sources of VOC and ammonia are not required to be evaluated for control measures in each area, unless the State or EPA provide a technical demonstration showing that emissions from sources in the State significantly contribute to PM2.5 concentrations in a specific area Rule provides basic guidance on potential analyses for technical demonstration; weight of evidence approach.

13 Fine Particle Composition

Emission Inventories Statewide inventory every 3 years per CERR (e.g. 2008, 2011) –Direct PM (incl. condensable PM), NOx, SO2, VOC, ammonia, CO Inventories for attainment planning –Base year (2008?) and projection year (2014?) inventories –Seasonal inventories may be appropriate for certain areas –Based on ambient monitoring data and other analyses, more highly resolved emissions estimates are needed for which key categories? Organic carbon: wood smoke, mobile sources, industry Ammonium nitrate: mobile sources, industry, ammonia sources? Tools for estimating emissions –MOVES and NONROAD models for mobile sources –EPA wood stove and fireplace emissions calculator –PM emissions inventory resource center 14

15 Reasonably Available Control Technology (RACT) / Reasonably Available Control Measures (RACM) For nonattainment areas, States need to adopt all reasonably available control measures (including RACT) needed to attain the standards as expeditiously as practicable and to meet reasonable further progress requirements –Collective analysis; demonstrate that there are no additional measures that are reasonably available and would enable the area to attain at least one year earlier Guidance in rule –Identify technically and economically feasible measures –Estimate improvement in air quality with modeling or other technique –Select RACT/RACM and adopt enforceable regulations Area-specific flexibility –No tonnage threshold; evaluate smaller sources for areas with more severe problem Preamble includes list of specific measures that States should consider as a starting point for RACT/RACM assessment

16 Example Emission Reduction Measures New or improved direct PM and precursor controls on stationary sources Diesel retrofits (trucks, school buses, stationary engines) Diesel idling (trucks, trains, port equipment, etc.) Programs to reduce emissions from poorly maintained vehicles Year-round operation of seasonal stationary source NOx controls Year-round measures to reduce vehicle miles traveled (carpooling incentives, etc.) Programs to reduce emissions from residential wood combustion, outdoor wood boilers, and back yard barrel burning Open burning laws and better enforcement Smoke management plans Reducing emissions of volatile aromatic compounds (surface coatings, gasoline, solvents, etc.) More information available at

EPA Guidance: Strategies for Reducing Residential Wood Smoke (October 2009) Public education –Burn as cleanly as possible: right wood, right way, right appliance –AIRNow real-time data and forecasting Wood Stove/Fireplace Changeouts and Removal –Changing out one old, dirty inefficient wood stove is equivalent to the fine particle pollution reduction of taking five diesel buses off the road. – Wood burning curtailment programs - examples –Sacramento: –Puget Sound: Outdoor wood boiler ordinance / regulation Guidance document available at: 17

Attainment Demonstration Analysis demonstrating that the area will attain as expeditiously as practicable based on best emissions estimates and control measure information available –Areas with substantial amount of secondary PM2.5 (e.g. nitrate) are recommended to use regional grid model; perhaps in combination with dispersion model for direct PM2.5 sources –Areas dominated by direct PM2.5 emissions – recommend use of dispersion model, or other approaches –For 24-hour standard, focus on days at high end of distribution –Unmonitored area analysis Identify attainment date for the area Ozone, PM2.5, and Regional Haze Modeling Guidance 18

19 Reasonable Further Progress (RFP) RFP: annual incremental reductions in emissions for purpose of ensuring timely attainment RFP plan is due with attainment demonstration If attainment date is no later than 5 years from designations (up to 2014), RFP is met by attainment demo For areas proposing an attainment date more than 5 years from designations, the State must establish emission reduction milestones for 2014 (and 2017 if applicable) showing “generally linear” progress from the base year through the attainment year Alternate reductions amounts by pollutant are possible if they would achieve equivalent air quality improvement Base year for RFP inventory should be same as for attainment demo Mid-course review due in 2016 for areas with attainment date in year 9 or 10 from designations (2018 or 2019) Evaluate progress in terms of emission reductions, ambient air quality, and implementation of measures Adopt new strategies as necessary

20 Contingency Measures Measures to be implemented without further action if area fails to attain by its attainment date or fails to meet RFP requirements. Need to be measures other than those required for attainment or to meet RFP Level of reductions: equal to one year’s worth of reductions needed to show attainment for the area –Example: if base year is 2008 and attainment year is 2014, then contingency measures should be equal to one-sixth of reductions (by pollutant) needed to show attainment, or provide for one-sixth of air quality improvement needed for attainment

Black Carbon and Climate Change ** Recent estimates indicate that the global warming impact of black carbon may be larger than any GHG other than CO2 Sources: IPCC 2007; Ramanathan and Carmichael, 2008.

Black Carbon and Climate Change Important climate co-benefits can be achieved (particularly in regions with snow and ice) with reductions of conventional air pollutants (such as black carbon, methane, and ozone) to address public health concerns EPA Report to Congress on Black Carbon (mid-2011) UNEP Integrated Assessment of Black Carbon and Tropospheric Ozone - Summary for Decision Makers (issued 2/17/11) See: UN Convention on Long-Range Transboundary Air Pollution Arctic Council 22

Near Salt Lake City, 11/17/09, 35 ug/m3 For more information: Rich Damberg (919)