Indiana Department of Environmental Management 2013 Ozone Season Summary Report Office of Air Quality (800) 451-6027 www.idem.IN.gov/airquality/2391.htm.

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Presentation transcript:

Indiana Department of Environmental Management 2013 Ozone Season Summary Report Office of Air Quality (800)

2013 Ozone Season Purpose This Ozone Season Summary Report provides an overview of ozone levels from 2013, as well as ozone trends over the last ten years (2004 through 2013). Summary The ozone season in Indiana lasts from April 1 through September 30. The duration of the ozone season for each state is mandated by the United States Environmental Protection Agency (U.S. EPA). 183 total days in Indiana’s 2013 ozone season. 4 exceedance days in forecasted days (Air Quality Action Days) in

Background of Ground-level Ozone What is ground-level ozone? Ground-level ozone is a gas composed of three oxygen atoms. The chemical structure of ozone is the same whether at ground level or above the earth, but it is unhealthy to breathe at ground level. Where does ground-level ozone come from? Ground-level ozone is not emitted directly into the air, but is created by a chemical reaction between nitrogen oxides (NO x ) and volatile organic compounds (VOCs) in the presence of sunlight. Emissions from industrial facilities and electric utilities, motor vehicle exhaust, gasoline vapors, and chemical solvents are some of the major sources of NO x and VOCs. Health effects of ground-level ozone: Chest pain, coughing, throat irritation, congestion. Can worsen bronchitis, emphysema, asthma. Reduces lung function and inflames the linings of the lungs. Scars lung tissues. 3

National Ambient Air Quality Standards (NAAQS) for Ozone Primary Standards Primary standards, also known as health standards, are limits set to protect public health, including the health of “sensitive” populations such as asthmatics, children, and the elderly. Secondary Standards Secondary standards are set to protect public welfare, including protection against decreased visibility, damage to animals, crops, vegetation, and buildings. 4

History of the Ozone Standard U.S. EPA first established a 1-hour standard of 0.08 parts per million (ppm) for ground-level ozone U.S. EPA revised the 1-hour ozone standard to a level of 0.12 ppm U.S. EPA replaced the 1-hour standard with an 8-hour health standard of 0.08 ppm Three states and industry challenged the new standard U.S. Supreme Court upheld the hour health standard for ozone hour health standard for ozone became effective U.S. EPA revoked the 1-hour ozone standard U.S. EPA strengthened the 8- hour health standard for ozone to a level of ppm U.S. EPA announced it would reconsider the hour health standard U.S. EPA announced it would move forward with implementation of the hour health standard set at a level of ppm U.S. EPA announced it would withdraw its reconsideration of the hour health standard and revisit the standard during the next statutorily required NAAQS review cycle slated for 2013

Attaining the Standard 8-Hour Standard To attain the 8-hour standard, the three-year average of the fourth (4 th ) highest daily maximum value for the ozone season must be at or below the standard of ppm. Exceedance versus a Violation of the Standard An exceedance occurs when an 8-hour average value is measured above the standard. A violation occurs when the three-year average of the 4 th highest daily maximum value for the ozone season exceeds the standard. A monitor can exceed the standard without being in violation. 6

Attainment Status Hour Ozone Health Standard U.S. EPA revised the former health standard in 1997 to 0.08 ppm. Attainment designations became effective in Initially, 23 counties and one township in Indiana were classified as being in violation of the standard. At the close of the 2008 ozone season, all Indiana counties met the standard. By May 2010, all areas were officially designated attainment under the standard Hour Ozone Health Standard U.S. EPA revised the 1997 health standard in 2008 to ppm. In March 2009, the Indiana Department of Environmental Management (IDEM) submitted state recommendations to U.S. EPA for attainment status for the 2008 standard. Based on monitoring data from 2006 through 2008, IDEM recommended 12 counties be designated as nonattainment. In September 2009, U.S. EPA announced it would reconsider the standard. 7

Attainment Status Hour Ozone Health Standard (continued) In September 2011, U.S. EPA announced it would withdraw its reconsideration of the 2008 standard and revisit the standard during the next statutorily required NAAQS review cycle slated for On September 22, 2011, U.S. EPA announced its intention to fast-track initial area designations and classification rule. Initial area designations were based on 2008 through 2010 air quality monitoring data and 2009 state recommendations. U.S. EPA also announced it would consider 2011 data if certified early (i.e., by February 15, 2012). U.S. EPA completed designations for the Chicago-Naperville, IL-IN-WI area on May 31, 2012, (2008 through 2010 monitoring data for Indiana and Wisconsin and 2009 through 2011 monitoring data for Illinois). All other area designations were completed on April 30, Lake and Porter counties and Dearborn County (Lawrenceburg Township) were designated nonattainment effective July 20, All other areas of the state were classified as unclassifiable/attainment. Lake and Porter counties are pending redesignation with U.S. EPA. 8

2013 Indiana Ozone Nonattainment Areas 9

Ozone (O 3 ) 8-Hour Design Values Ozone 8-Hour Design Values (3-Year Average 4 th High Daily Maximum) Based on 2011 through 2013 Monitoring Data Standard at ppm 10

2013 Monitoring Network Placement U.S. EPA provides guidance on placement of monitors. Monitors placed based on population density and manufacturing levels. Monitors 41 ozone monitors in 27 counties across Indiana. Calculating the Monitoring Data Levels are monitored 24 hours per day and rolling 8-hour averages are calculated; highest 8-hour average is reported for the day. A monitor’s design value is calculated at the end of each ozone season; design values are calculated for each monitor in the state. –Design value: three-year average of fourth highest daily maximum values. 11

2013 Monitoring Summary No monitors in the state recorded annual 4 th high daily maximum values above the hour health standard, i.e., greater than ppm. The Charlestown State Park, Michigan City, New Albany, and Plummer ozone monitors had three-year average 4 th high daily maximum design values for the years 2011 through 2013 that exceeded the hour health standard. 12

Ozone Monitors by Area 13 AreaCounties Northwest Lake LaPorte Porter North Central Elkhart St. Joseph Northeast Allen Huntington Central Boone Johnson Delaware Madison Hamilton Marion Hancock Morgan Hendricks Shelby West Central Carroll Vigo Southwest Greene Vanderburgh Perry Warrick Posey Southeast Clark Jackson Floyd

Annual 4 th High Trends Hour Health Standard Hour Health Standard

Design Value Trends Hour Health Standard Hour Health Standard

Meteorologically Adjusted Trend Analysis In order to account for variable meteorology, IDEM conducted a meteorologically adjusted trend analysis. Meteorological conditions can play an important role in ozone formation. By comparing ozone values under similar meteorological conditions, IDEM can evaluate whether trends are a result of changes in ozone precursor emissions and/or changes in meteorology. The results of this analysis confirm a downward trend in monitored ozone values across the state through Meteorological data used to conduct this analysis is through the year 2012, as 2013 data is not available until well after the end of the ozone monitoring season. Detailed information concerning this analysis is included in the appendix. 16

Additional Information For additional information regarding the NAAQS for ground- level ozone, please visit U.S. EPA’s Ground-level Ozone Regulatory Actions website:

Contact For more information regarding the ozone designation process, or Indiana’s redesignation petitions and maintenance plans, visit or contact Mr. Gale Ferris of the Office of Air Quality at (800) , (317) , or 18

APPENDIX Meteorologically Adjusted Trend Analysis Results A-1

Analysis Results A-2 Central Indiana Important nodes are those that contain individual monitoring values over ppm: Fort Benjamin Harrison (Nodes 13 & 50) and Bristol (Nodes 12 & 13). North Central Indiana

Analysis Results A-3 Important nodes are those that contain individual monitoring values over ppm: Beacon Street (Nodes 9, 13, 25 & 29) and Ogden Dunes (Nodes 13 & 29). NortheastNorthwest

Analysis Results A-4 SoutheastSouthwest Important nodes are those that contain individual monitoring values over ppm: Charlestown (Nodes 10, 11 & 18) and Evansville (Nodes 20 & 42). Node 20 at the Evansville monitor contains values for 2010 and 2011 only, which meet conditions of that node; the dataset for Node 20 contains one value over the standard in June 2011.

Analysis Results A-5 Rural Background Important nodes are those that contain individual monitoring values over ppm: Plummer (Nodes 4, 13, 25, 29, 42 & 56).