Rice University Tropospheric Ozone Pollution Project (RU-TOPP) Gary A. Morris.

Slides:



Advertisements
Similar presentations
Department of the Environment The Basic Science of Air Pollution Transport Brian J. Hug Division Chief, Air Quality Planning and Policy Division.
Advertisements

Improving the View of Air Quality from Space Jim Crawford Science Directorate NASA Langley.
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.
NASA AQAST 6th Biannual Meeting January 15-17, 2014 Heather Simon Changes in Spatial and Temporal Ozone Patterns Resulting from Emissions Reductions: Implications.
Template Review of Northeast Texas 2012 Ozone Season Presentation to the NETAC Policy and Technical Committees June 13, 2013 Sue Kemball-Cook, Wilson Santamaria.
Introduction to Ozone Nate Herbst Southern Ute Indian Tribe.
Modeling Guidance and Examples for Commonly Asked Questions (Part II) Reece Parker and Justin Cherry, P.E. Air Permits Division Texas Commission on Environmental.
Western Regional Ozone Issues Observations and concerns Changing perspective- not all isolated ozone issues Trends in Colorado areas Near non-attainment.
REDUCTION OF HIGHLY REACTIVE VOLATILE ORGANIC COMPOUNDS & VARIABLE EMISSIONS IN HOUSTON/GALVESTON: MONITORING, MODELING, MEASURING, RULEMAKING David Allen.
Click to edit Master title style Click to edit Master subtitle style 1 Modeling of 1,3-Butadiene for Urban and Industrial Areas B. Rappenglück and B. Czader.
CO budget and variability over the U.S. using the WRF-Chem regional model Anne Boynard, Gabriele Pfister, David Edwards National Center for Atmospheric.
METO 621 CHEM Lesson 6. A Typical Day in a Pollution Episode A common severe pollution weather pattern occurs when high pressure is centered just west.
Bay breeze enhanced air pollution event in Houston, Texas during the DISCOVER-AQ field campaign Christopher P. Loughner (University of Maryland) Melanie.
Houston Regional Monitoring HRM Houston Regional Monitoring Network Overview.
Variability in Ozone Profiles at TexAQS within the Context of an US Ozone Climatology Mohammed Ayoub 1, Mike Newchurch 1 2, Brian Vasel 3 Bryan Johnson.
METO 637 Lesson 19. NO x emission inventory VOC Emissions.
AREHNA Workshop-Mobility and Health, 3-6 May 2003, Kos, Greece Assist. Professor Dr. A. PAPAYANNIS Lasers and Applications Laboratory National Technical.
Prepared by Hilary Hafner, Daniel Alrick, ShihMing Huang, and Adam Pasch Sonoma Technology, Inc. Petaluma, CA Presented at the 2010 National Air Quality.
Missouri Air Quality Issues Stephen Hall Air Quality Analysis Section Air Pollution Control Program Air Quality Applied Sciences Team (AQAST) 9 th Semi-Annual.
OTAG Air Quality Analysis Workgroup Volume I: EXECUTIVE SUMMARY Dave Guinnup and Bob Collom, Workgroup co-chair “Telling the ozone story with data”
Air Quality Challenges In South Central Texas Issues and Demand to Infrastructure in the Eagle Ford Region Eagle Ford Consortium Peter Bella, Natural Resources.
National Aeronautics and Space Administration Jet Propulsion Laboratory California Institute of Technology Tropospheric Emission Spectrometer Evaluating.
A&WMA Georgia Regulatory Update Conference Current State of the Air in GA Jac Capp, GA EPD, Branch Chief, Air Protection Branch April 16, 2013.
Great Basin Ozone Problem Measurements indicate high ozone concentrations in the Great Basin. Back trajectory analysis and satellite remote sensing will.
New York City Case Study: Methods of Analysis David J. Nowak USDA Forest Service Northeastern Research Station Syracuse, NY.
Lindsey Kuettner and Dr. Patricia Cleary  Department of Chemistry  University of Wisconsin-Eau Claire Back Trajectory Analysis and Measurement of Ozone.
CENRAP’s RPO Meeting Ileana Isern-Flecha, et.al March 31, 2004 Technical Analysis Division Texas Air Quality Study (TexAQS) II ( )
Tom Ryerson NOAA ESRL Chemical Sciences Division CalNex 2010: NOAA perspective Goal of this presentation:
Urban Air Pollution Public and Environmental Health Concerns –Elevated levels of toxic compounds Regional and Global Impacts –Background Chemistry and.
Importance of Lightning NO for Regional Air Quality Modeling Thomas E. Pierce/NOAA Atmospheric Modeling Division National Exposure Research Laboratory.
Research and Development to Meet Urban Weather and Climate Needs Dr. Richard D. Rosen NOAA Research September 23, 2004 Presentation at “Challenges in Urban.
The Pattern and Transport of Ozone in the Missouri Region Rudolf Husar and Bret Schichtel CAPITA Washington University April 9, 1997 Prepared for a briefing.
WRPLOT View & “Some” Wind Rose Uses Glenn Gehring, Technology Specialist III Tribal Air Monitoring Support Center
Presentation by: Dan Goldberg Co-authors: Tim Vinciguerra, Linda Hembeck, Sam Carpenter, Tim Canty, Ross Salawitch & Russ Dickerson 13 th Annual CMAS Conference.
Determining Alternative Futures - Urban Development Effects on Air Quality Julide Kahyaoglu-Koracin and Darko Koracin May 2007 Zagreb, Croatia.
Estimating local versus regional contributions to tropospheric ozone: An example case study for Las Vegas Mark Green and Dave DuBois Desert Research Institute.
Latvian Environmental, Geology and Meteorology agency Future development scenarios for traffic system and air pollution in Riga city Iveta Steinberga La.
Modeling Compliance with the 8-Hour Standard Jay Olaguer Houston Advanced Research Center 10/06/04.
Impact of Biodiesel in Ozone Production in Atlanta Siv Balachandran EAS /24/07 Siv Balachandran EAS /24/07.
Spatial Pattern of PM2.5 over the US PM2.5 FRM Network Analysis for the First Year: July 1999-June 2000 Prepared for EPA OAQPS Richard Scheffe by Rudolf.
Why is Ozone Low in Baltimore City? In most cities, ozone is lower in city centers than it is downwind of the cities –Well established in the scientific.
The Clean Air Act First Clean Air Act passed in 1967: 1970 Amendments established current relationship between states and federal government and required.
Why is the Low Level Jet Important to the Baltimore/DC Region? MWAQC-TAC Meeting January 21, 2005.
Visual Correlation between Air Pollution and Population Density in Major Metropolitan Areas Texas A&M University, Department of Civil Engineering, Applications.
Melanie Follette-Cook (MSU/GESTAR) Christopher Loughner (ESSIC, UMD) Kenneth Pickering (NASA GSFC) Rob Gilliam (EPA) Jim MacKay (TCEQ) CMAS Oct 5-7, 2015.
Goal: “What are the sources and physical mechanisms that contribute to high ozone concentrations aloft that have been observed in Central and Southern.
August 1999PM Data Analysis Workbook: Characterizing PM23 Spatial Patterns Urban spatial patterns: explore PM concentrations in urban settings. Urban/Rural.
Brad Miller Anna Kelley. National Ambient Air Quality Standard Update New Sulfur Dioxide Non-Attainment Area – Effective October 4, 2013 Ozone Secondary.
NAAQS and Criteria Pollutant Trends Update US EPA Region 10.
Ozone Transport that Impacts on Tribal Land: Case Study Stan Belone Salt River Pima-Maricopa Indian Community.
CARB Board Meeting San Diego, 23 July 2009 DAVID PARRISH Chemical Sciences Division Earth System Research.
Bret A. Schichtel Center for Air Pollution Impact and Trend Analysis (CAPITA) Washington University St. Louis, MO, Presented at EPA’s National Exposure.
1. How is model predicted O3 sensitive to day type emission variability and morning Planetary Boundary Layer rise? Hypothesis 2.
Initial task : examine the impacts air pollution governance in Houston in the transportation sector What is the structure of air pollution governance.
August 1999PM Data Analysis Workbook: Characterizing PM1 Characterizing Ambient PM Concentrations and Processes What are the temporal, spatial, chemical,
Air Quality in Texas Birnur Guven Houston Advanced Research Center June 23, 2010 – Johnson Space Center.
Influence of Lightning-produced NOx on upper tropospheric ozone Using TES/O3&CO, OMI/NO2&HCHO in CMAQ modeling study M. J. Newchurch 1, A. P. Biazar.
August 1999PM Data Analysis Workbook: Characterizing PM23 Spatial Patterns Urban spatial patterns: explore PM concentrations in urban settings. Urban/Rural.
Fire impacts – Natural event data exclusions/ozone monitoring Colleen Delaney, Utah Division of Air Quality March 11, 2004.
Preliminary Analysis by: Fawn Hornsby 1, Charles Rogers 2, & Sarah Thornton 3 1,3 North Carolina State University 2 University of Texas at El Paso Client:
NAAQS Status in GA & PSD Inventory Update James W. Boylan Georgia EPD – Air Protection Branch Manager, Planning & Support Program AWMA Regulatory Update.
Ozone Budget From: Jacob. Ozone in the Atmosphere Lifetime: –~1 month –Highly variable – dependent on season, latitude, altitude, etc. Background concentrations:
AOSC 200 Lesson 27. A Typical Day in a Pollution Episode A common severe pollution weather pattern occurs when high pressure is centered just west of.
Smog “Trends” -- Atlanta and Elsewhere Annual Peak Observed Concentration, EPD, US EPA.
Satellite Data for Health & Air Quality Applications
Daily Screening for Wildfire Impacts on Ozone using a Photochemical Model A Proposal to the Texas Near-Nonattainment Areas Greg Yarwood
Paul Kelley1,2, Winston Luke2, Xinrong Ren1,2
Shell Center for Sustainable Development Seminar
Dave DuBois New Mexico State University
Planning to Achieve the 8-Hour Ozone Standard
Presentation transcript:

Rice University Tropospheric Ozone Pollution Project (RU-TOPP) Gary A. Morris

1)Motivation 2)Work to Date 3)Future of Project Rice University Tropospheric Ozone Pollution Project (RU-TOPP) Gary A. Morris

Environmental Threats and Health Impacts Caused by Ozone Pollution Exacerbate/Cause Respiratory Problems Damaging to Plants Highly Reactive Can Be Transported Over Long Distances

Economic Impacts from Ozone Pollution Loss of Federal Transportation Funds $30,000 per day fines to all stationary sources Factor in locating business offices Factor in attracting workers

Current EPA Standards Only Address Ground-Level Ozone Stage 1: 1-Hour Standard Region must not exceed 125 ppb on more than 3 days in a consecutive 3-year period. Deadline: 2007 Stage 2: 8-Hour Standard Region must not exceed 85 ppb for the 3-year average of the 4 th highest daily maximum 8-hour ozone concentration. Deadline: 2010

Houston Regularly Violates Both Standards August 21 – September 2, 2000

20-Year Record Shows Improvement But We’re Not There Yet Hour 1-Hour

Areas at Risk in the United States Severe Risk Chicago, Houston, Los Angeles, New York, Washington, DC Serious Risk Atlanta, Boston, Dallas, Hartford, Phoenix Moderate Risk Cincinnati EPA Non-Attainment Areas August 2003

Galveston Bay N Downtown Houston Industrial Complexes East Texas Forested (Evergreens) NASA Space Shuttle Photo from STS-61 Houston, Texas: A Case Study for Ozone Pollution

Dense Ground Monitoring Networks in Urban Areas are a Good Start PAMS Photochemical Assessment Monitoring Stations Ozone & Other Species Meteorological Data Hourly Data on Web Houston, Texas March 17, 2003

Winds Transport Ozone Pollution “Although many cities have made efforts to control ozone by reducing local emissions, incoming ozone transported from upwind areas also needs to be addressed.” (EPA)

Houston Exceeds L.A. Again in 2004 Last week’s Houston Chronicle reported that Houston will again surpass L.A. for the number of violations of EPA Air Quality standards in 2004.

EPA Studies O 3 Production in 5 Cities Nashville isolated city, biogenic sources, NOx emitters (power plants) Phoenix isolated, low biogenic, low industry, dry Philadelphia and NYC inter-urban transport Houston extensive industry, coastal

Houston Unique Among Cities in the EPA Study City Number of Flights Total O 3 > 100 O 3 > 120 Max O 3 (ppbv) Nashville (’95) NYC (’96) Phoenix (’98) Philadelphia (’99) Houston (’00) flights in Houston show ozone > 150 ppbv Data courtesy P. Daum (2003)

Data from TexAQS 2000 Indicate Ship Channel as Primary Source Region Courtesy P. Daum (2003) Flight data from TexAQS 2000 show highest ozone production rates co-located with industrial sector near Houston Ship Channel

Back-Trajectory Analysis Trace Plumes Back to Ship Channel Courtesy P. Daum (2003) Calculate back-trajectories. Black dots are 1-hr intervals. O 3 production: High Low “Without exception, back- trajectories from the locations where these high O 3 plumes were observed passed over, or in close proximity to, sources of NO x and hydrocarbons surrounding the Houston Ship Channel.” Daum (2003). Latitude Longitude

Limitations of Current Ground-Level Ozone Monitoring Instrumentation No Information on Vertical Distribution of Ozone Transport (especially aloft) Not Well Monitored Few Rural Measurements

TexAQS 2000 Data Show Ozone Formation Above the Surface Down-looking lidar observers large plumes of ozone above the surface Ground monitors unable to detect this ozone pollution

telescope Ground-Based Ozone Lidar Would Provide Important Data Continuously monitor O 3 above the surface. Total magnitude of the pollution problem. O 3 aloft results in more persistent high levels of O 3 at the ground. Proposal to NSF in January 2005 High Powered UV Laser System O2O2 N2N2 O3O3

Shell Center for Sustainability Funds RU-TOPP in 2004 $40,000 grant Acquire ozonesonde laboratory Fly balloons to begin characterizing O 3 aloft. Undergraduate student participation

RU-TOPP Launches 25 Ozonesondes in July and August 2004 Nearly daily launches during peak pollution season Coordination with NASA Media attention: KHOU, the Houston Chronicle, National Public Radio…

Early Analysis Shows Impact of Remote Forest Fires July 19 th and 20th High ozone levels in Houston Air mass trajectories show air came from West Coast

Early Analysis Also Shows Local Production of Ozone Launches on Aug. 7 am & 2 pm Low levels in morning & High levels in afternoon Local production of ~600 tons of O 3 per day.

Sharing Data with NASA and the Scientific Community Data available on web: Part of NASA project to examine transport of pollution across U.S. and the Atlantic U. of Houston Models Proposals to NASA to continue this research.

Sustainability Assessment Through Continued Data Acquisition Continued monitoring of O 3 above Houston with regular flights Better understanding of O 3 problem: remote vs. local sources More effective solutions to meet the EPA 1-hour and 8-hour standards Community awareness

1)Motivation 2)Work to Date 3)Future of Project Rice University Tropospheric Ozone Pollution Project (RU-TOPP) Gary A. Morris