Indiana Department of Environmental Management Office of Air Quality (800) 451-6027 www.idem.IN.gov/6650.htm 2011 Ozone Season Summary Report 1.

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Presentation transcript:

Indiana Department of Environmental Management Office of Air Quality (800) Ozone Season Summary Report 1

2011 Ozone Season Purpose This Ozone Season Summary Report provides an overview of ozone levels from 2011, as well as ozone trends over the last ten years ( ). 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 2011 ozone season. 24 exceedance days in forecasted days (Air Quality Action Days) in Air Quality Action Day occurred in the month of October. 2

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. Background of Ground-Level Ozone 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 ppm Three states and industry challenged the new standard hour health standard for ozone became effective U.S. EPA significantly strengthened the health standard for ozone to a level of ppm U.S. Supreme Court upheld the hour health standard for ozone U.S. EPA revoked the 1-hour ozone standard U.S. EPA announced it would reconsider the hour health standard 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 U.S. EPA announced it would move forward with implementation of the hour health standard set at a level of ppm

8-Hour Standard To attain the 8-hour standard, the three-year average of the 4 th highest 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 value for the ozone season exceeds the standard. A monitor can exceed the standard without being in violation. Attaining the Standard 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 will be based on 2008 through 2010 air quality monitoring data and 2009 state recommendations. U.S. EPA is not requiring states to submit new recommendations data will be considered if certified early (i.e. by February 15, 2012). –Proposed designations late –Final designations early –Interstate urban areas of Indiana potentially affected (Chicago, Cincinnati, and Louisville).

Indiana Ozone Attainment Areas with a Maintenance Plan

10 Ozone 8-Hour Design Values (3-Year Average 4 th High) Based on Monitoring Data Standard at ppm

Monitoring 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 values. 11

2011 Monitoring Summary 12 The Charlestown State Park, Evansville, Fort Harrison, Michigan City, New Albany, Plummer, and St. Phillips ozone monitors recorded annual 4 th high values above the hour health standard of ppm (i.e. equal to or greater than ppm). No monitors in the state had a three-year average 4 th high design value that exceeded the hour health standard. None of Indiana’s maintenance areas classified under the hour health standard exceeded the warning or action level triggers.

Ozone Monitors by Area 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 13

Annual 4 th High Trends Hour Health Standard Hour Health Standard 14

Design Value Trends Hour Health Standard Hour Health Standard 15

Meteorologically Adjusted Trend Analysis 16 In order to account for variable meteorology, IDEM conducted a meteorologically adjusted trend analysis. This type of analysis is necessary to account for variability with critical meteorological conditions among ozone seasons, and verify upward or downward trends. The results of this analysis confirm a downward trend in ozone air quality across the state. Detailed information concerning this analysis is included in the appendix.

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. Shawn Seals of the Office of Air Quality at (800) , (317) , or 18

APPENDIX A-1 Meteorologically Adjusted Trend Analysis Results

CART Results A-2 Important nodes contain the most individual monitor values over ppm: Fort Benjamin Harrison (Node 13) and Bristol (Node 13). Central IndianaNorth Central Indiana

CART Results A-3 I mportant nodes contain the most individual monitor values over ppm: Beacon Street (Node 13) and Ogden Dunes (Node 13). Northeast IndianaNorthwest Indiana

CART Results A-4 Important nodes contain the most individual monitor values over ppm: Charlestown (Node 25) and Inglefield (Node 10). Southeast IndianaSouthwest Indiana

CART Results A-5 Important nodes contain the most individual monitor values over ppm: Plummer (Node 13). Rural Background