1 Asheville Air Quality Megan Stone. 2 Clean Smokestacks Act Passed in 2002 by the General Assembly of North Carolina Passed in 2002 by the General Assembly.

Slides:



Advertisements
Similar presentations
Estimated Mercury Emission Reductions in NC from Co- control as a Result of CSA 2004 NC DENR/DAQ Hg & CO2 Workshop Raleigh, NC April 20, 2004 Steve Schliesser.
Advertisements

Environmental Leadership The Pursuit of Cleaner Air
North Carolina Division of Air Quality - Mercury Regulations, Emissions, and Deposition Modeling in North Carolina Presented for 6th Annual Unifour Air.
Heather Simon, Adam Reff, Benjamin Wells, Neil Frank Office of Air Quality Planning and Standards, US EPA Ozone Trends Across the United States over a.
Emissions Reductions Beyond the Clean Smokestacks Act (CSA) Emissions Reductions Beyond the Clean Smokestacks Act (CSA) Environmental Management Commission.
1 Policies for Addressing PM2.5 Precursor Emissions Rich Damberg EPA Office of Air Quality Planning and Standards June 20, 2007.
Three-State Air Quality Study (3SAQS) Three-State Data Warehouse (3SDW) 2008 CAMx Modeling Model Performance Evaluation Summary University of North Carolina.
Ozone in Colorado: Issues and Reduction Strategies Presentation to the Colorado Environmental Health Association October 2,
Integration of CMAQ into the Western Macedonia environmental management system A. Sfetsos 1,2, J. Bartzis 2 1 Environmental Research Laboratory, NCSR Demokritos.
Solutions: Preventing and Reducing Air Pollution
ATMOSPHERIC CHEMISTRY: FROM AIR POLLUTION TO GLOBAL CHANGE AND BACK Daniel J. Jacob.
Air Pollution.
Minnesota’s Ethanol Experience What we know, -A 10% ethanol blend has 3.5% oxygen. -More oxygen than any other oxygenate. -Ethanol helped MN. achieve compliance.
Air Quality Beyond Ozone and PM2.5 Sheila Holman North Carolina Division of Air Quality 6 th Annual Unifour Air Quality Conference June 15, 2012.
1 Emission and Air Quality Trends Review Washington July 2013.
Progress Energy and the Environment Western North Carolina Air Quality Don Cooke April 29, 2003.
North Carolina Division of Air Quality Report on Control of Mercury Emissions from Coal-Fired Electric Generating Units In response to 15 NCAC 02D.2509(b)
ERCOT 2003 UFE ANALYSIS By William Boswell & Carl Raish AEIC Load Research Conference July 13, 2005.
Air Quality Impact Analysis 1.Establish a relationship between emissions and air quality. AQ past = a EM past + b 2.A change in emissions results in an.
1 Emission and Air Quality Trends Review Nevada May 2013.
Chapter 14 – Correlation and Simple Regression Math 22 Introductory Statistics.
College of Engineering Update for Agilent Impacts of Emission Changes on Air Quality and Acute Health Effects in the Southeast, 1993 – 2012 Lucas Henneman.
EFFICIENT CHARACTERIZATION OF UNCERTAINTY IN CONTROL STRATEGY IMPACT PREDICTIONS EFFICIENT CHARACTERIZATION OF UNCERTAINTY IN CONTROL STRATEGY IMPACT PREDICTIONS.
Forty-five Years of the Clean Air Act Ron Gore ADEM August,2015.
UFE 2003 Analysis June 1, UFE 2003 ANALYSIS Compiled by the Load Profiling Group ERCOT Energy Analysis & Aggregation June 1, 2005.
Global Ozone Project Curriculum
Ground Level Ozone By: Sohan Pillarisetti & Jason Soong.
Henry Hogo Assistant Deputy Executive Officer Mobile Source Division Science and Technology Advancement 2015 International Emission Inventory Conference.
Assessment of Mercury Rules for Electric Generators in North Carolina September 9, 2015 Presented to the Environmental Management Commission – Air Quality.
Ramifications of Charlotte Regional Growth and Weekday Activities on Primary and Secondary Emissions Jenny L. Perry and Patrick M. Owens Department of.
Indian Power-plant NO x Emissions from OMI and Inventories David Streets and Zifeng Lu Argonne National Laboratory Argonne, IL AQAST-3 Meeting University.
Modeling of Ammonia and PM 2.5 Concentrations Associated with Emissions from Agriculture Megan Gore, D.Q. Tong, V.P. Aneja, and M. Houyoux Department of.
1 Emission and Air Quality Trends Review Connecticut July 2013.
Section 4-4 Air Pollution and Solutions 1.What are the causes of smog and acid rain? 2.What are the causes of indoor air pollution? 3.What is the key to.
Wildland Fire Impacts on Surface Ozone Concentrations Literature Review of the Science State-of-Art Ned Nikolov, Ph.D. Rocky Mountain Center USDA FS Rocky.
Presented at the AQAST 9 th Semiannual Meeting Wednesday June 3 rd, 2015 Presentation by: Dan Goldberg, Ph.D. Candidate Co-authors: Tim Canty, Tim Vinciguerra,
INTERCONTINENTAL TRANSPORT OF OZONE AND ITS SEASONAL VARIATIONS IN EUROPE Dick Derwent rdscientific 2 nd ICAP Workshop Chapel Hill, North Carolina October.
2.5 Using Linear Models A scatter plot is a graph that relates two sets of data by plotting the data as ordered pairs. You can use a scatter plot to determine.
Progress Energy Issues Overview April 25, 2006 Don Cooke Sr. Environmental Coordinator.
1 Emission and Air Quality Trends Review North Dakota July 2013.
Opening Remarks -- Ozone and Particles: Policy and Science Recent Developments & Controversial Issues GERMAN-US WORKSHOP October 9, 2002 G. Foley *US EPA.
Climatic implications of changes in O 3 Loretta J. Mickley, Daniel J. Jacob Harvard University David Rind Goddard Institute for Space Studies How well.
1 Emission and Air Quality Trends Review New Hampshire July 2013.
1 Emission and Air Quality Trends Review Idaho July 2013.
Reasonable Further Progress Policy and Mid-Course Reviews John Summerhays EPA Region 5 June 20, 2007.
CHAPTER 12.1 ENVIRONMENTAL SCIENCE What Causes Air Pollution?
Breakout Session 1 Air Quality Jack Fishman, Randy Kawa August 18.
Emission reductions needed to meet proposed ozone standard and their effect on particulate matter Daniel Cohan and Beata Czader Department of Civil and.
The Double Dividend of Methane Control Arlene M. Fiore IIASA, Laxenburg, Austria January 28, 2003 ANIMALS 90 LANDFILLS 50 GAS 60 COAL 40 RICE 85 TERMITES.
ORIGIN OF BACKGROUND OZONE IN SURFACE AIR OVER THE UNITED STATES: CONTRIBUTION TO POLLUTION EPISODES Daniel J. Jacob and Arlene M. Fiore Atmospheric Chemistry.
1 Emission and Air Quality Trends Review North Carolina May 2013.
Background ozone in surface air over the United States Arlene M. Fiore Daniel J. Jacob US EPA Workshop on Developing Criteria for the Chemistry and Physics.
Urban air pollution and Acid rain. Pollutants Primary – emitted directly exhaust fumes factory chimneys Oil spills Secondary – primary reacts with substances.
Emission and Air Quality Trends Review
Smog/Ground level ozone
Sunil Kumar TAC, COG July 9, 2007
16.3 Categories of Air Pollutants
Emission and Air Quality Trends Review
The Double Dividend of Methane Control
Department of Environmental Quality
Jenny L. Perry and Patrick M. Owens Department of Chemistry
Within-Week Variability and Long-Term Trends in Traffic, Power Plant Emissions, and Ambient CO, NOy and Ozone for the Charlotte Metropolitan Area Jennifer.
AIR POLLUTION AND GLOBAL CHANGE: TOWARDS AN INTEGRATED POLICY
Uncertainties influencing dynamic evaluation of ozone trends
Emission and Air Quality Trends Review
Emission and Air Quality Trends Review
Diagnostic and Operational Evaluation of 2002 and 2005 Estimated 8-hr Ozone to Support Model Attainment Demonstrations Kirk Baker Donna Kenski Lake Michigan.
Emission and Air Quality Trends Review
Emission and Air Quality Trends Review
Energy Transformation and Fuels (p 226)
Presentation transcript:

1 Asheville Air Quality Megan Stone

2 Clean Smokestacks Act Passed in 2002 by the General Assembly of North Carolina Passed in 2002 by the General Assembly of North Carolina “An act to improve air quality in the state by imposing limits on the emission of certain pollutants from certain facilities that burn coal to generate electricity…” “An act to improve air quality in the state by imposing limits on the emission of certain pollutants from certain facilities that burn coal to generate electricity…”

3 Clean Smokestacks Act Requires Progress Energy and Duke Energy to submit annual reports containing air quality information. Requires Progress Energy and Duke Energy to submit annual reports containing air quality information. Progress Energy has spent $190 million dollars at the Asheville plant for technologies to reduce emissions. Progress Energy has spent $190 million dollars at the Asheville plant for technologies to reduce emissions.

4 Clean Smokestacks Act Western North Carolina has a huge ozone problem. Western North Carolina has a huge ozone problem. Cutting NOx emissions would reduce the amount of ozone in the area. Cutting NOx emissions would reduce the amount of ozone in the area. Scrubbers have been installed in the Asheville Power Plant Scrubbers have been installed in the Asheville Power Plant

5 Formation of Ozone

6 Scrubbers NOx + NH 4  H 2 O(g) + N 2

7

8

9

10 Correlation Coefficient Measures the linear relationship between two variables. Measures the linear relationship between two variables. The correlation coefficient (r 2 ) is always between -1 and +1. The closer the correlation is to +/-1, the closer to a perfect linear relationship. The correlation coefficient (r 2 ) is always between -1 and +1. The closer the correlation is to +/-1, the closer to a perfect linear relationship.

11 Correlation Coefficient Ozone vs. Sunlight Ozone vs. Sunlight Ozone vs. VOCs Ozone vs. VOCs Ozone vs. NOx Ozone vs. NOx

12 Sunlight vs. Ozone Hypothesis: More sunlight yields more ozone. Hypothesis: More sunlight yields more ozone. Therefore, R 2 > 0 for a correlation between ozone and sunlight amount. Retrieved daily “clear” observations for 2006/2007 summers from NCDC  calculated daily percentages (10am, 1pm, and 4pm) Retrieved daily “clear” observations for 2006/2007 summers from NCDC  calculated daily percentages (10am, 1pm, and 4pm)

13

April May June July August September October Monthly Sunlight %Ozone (ppm)

15

April May June July August Sept Oct Monthly Sunlight % Ozone (ppm)

17 Sunlight vs. Ozone 2006: R 2 =  Practically no correlation 2006: R 2 =  Practically no correlation 2007: R 2 =  Much stronger positive correlation 2007: R 2 =  Much stronger positive correlation Conclusion: Both are positive correlations. Conclusion: Both are positive correlations. (But what happened in 2006?)

18 Ozone vs. VOCs The state of NC releases estimates of how much VOCs are released by humans per month every three years. The state of NC releases estimates of how much VOCs are released by humans per month every three years. VOCs are not monitored. VOCs are not monitored. Hypothesis: An increase of VOCs yields an increase of ozone. Therefore, R 2 > 0 for a correlation between ozone and VOCs. Hypothesis: An increase of VOCs yields an increase of ozone. Therefore, R 2 > 0 for a correlation between ozone and VOCs.

19

MonthOzoneVOC April May June July August Sept Oct R 2 R 2 =

21 NOx vs. Ozone Like VOCs, NOx emissions are not monitored like ozone. Like VOCs, NOx emissions are not monitored like ozone. Division of Air Quality releases estimates of how much the Asheville Plant emits monthly every three years. Division of Air Quality releases estimates of how much the Asheville Plant emits monthly every three years. Last time was 2005 (before any scrubbers were installed) Last time was 2005 (before any scrubbers were installed)

22 NOx vs. Ozone Hypothesis: An increase of NOX yields an increase of ozone. Hypothesis: An increase of NOX yields an increase of ozone. Therefore, R 2 > 0 for a correlation between ozone and NOx. Therefore, R 2 > 0 for a correlation between ozone and NOx.

23

NOx vs. Ozone MonthOzoneNox April May June July August Sept Oct R 2 R 2 = Negative correlation??????????

25 Explanation Sunlight reacts with NOx Sunlight reacts with NOx NOx + sunlight  NO + O O + O 2  O 3

26 Explanation The ozone created from this reaction then reacts with more NOx… NOx + O 3  NOx + O 2 No net gain or loss of ozone!

27 Explanation It’s the addition of VOCs into the atmosphere that alters the chemistry which contributes to elevated levels of ozone. It’s the addition of VOCs into the atmosphere that alters the chemistry which contributes to elevated levels of ozone. NOx + VOC + sunlight  O 3

28 Ozone Prediction Predicting ozone levels is a lot more complicated than what we think. Predicting ozone levels is a lot more complicated than what we think.

29 New Hypothesis In order to reduce ozone levels, we must reduce the sunlight or VOC amounts… In order to reduce ozone levels, we must reduce the sunlight or VOC amounts… We cannot stop sunlight, so in order to decrease ozone, we must accompany the NOx reduction with a VOC reduction. We cannot stop sunlight, so in order to decrease ozone, we must accompany the NOx reduction with a VOC reduction. Is it possible? Is it possible?

30 The Future Analysis of 2008 data – is there still a negative correlation between NOx and Ozone? Analysis of 2008 data – is there still a negative correlation between NOx and Ozone? Why was there a natural decreasing trend in ozone? Why was there a natural decreasing trend in ozone? Possibility of a lag? Possibility of a lag?

31 References Tropospheric Air Pollution: Ozone, Airborne Toxics, Polycuclic Aromatic Hydrocarbons, and Particles. Pitts & Pitts Tropospheric Air Pollution: Ozone, Airborne Toxics, Polycuclic Aromatic Hydrocarbons, and Particles. Pitts & Pitts Statistical Methods in the Atmospheric Sciences. Daniel S. Wilkes Statistical Methods in the Atmospheric Sciences. Daniel S. Wilkes North American Mesoscale Model – Community Multiscale Air Quality Model Ozone Forecast Verification Study For Knoxville, TN (Summer 2005). Loren C. Marz North American Mesoscale Model – Community Multiscale Air Quality Model Ozone Forecast Verification Study For Knoxville, TN (Summer 2005). Loren C. Marz