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

Slides:



Advertisements
Similar presentations
AREP GURME Section 11 Case Studies of Episodes What is a Case Study? How to Conduct Case Studies Examples.
Advertisements

Reducing Air Pollution Challenges and Opportunities New Jersey Clean Air Council April 14, 2010.
Ch. 1, Sec. 2 North Carolinas Climate and Weather Assess the impact of geography on the settlement and developing economy of the Carolina economy.
Maryland Department of the Environment
Wind and Weather.
Ozone Season Summary 2012 Sunil Kumar ACPAC September 10, Item #4.
Department of the Environment What Will It Take? DG Stakeholder Meeting - June 24, 2013 Meeting the New Ozone Standard.
CE Introduction to Environmental Engineering and Science Readings for This Class: O hio N orthern U niversity Introduction Chemistry, Microbiology.
Historic Winter Storm/Blizzard February 8-9, 2013 Historic Winter Storm/Blizzard February 8-9, 2013 Updated Headlines: 4 PM Thursday, February 7 th, 2013.
Once released, pollutants are free to wander
NASA AQAST 6th Biannual Meeting January 15-17, 2014 Heather Simon Changes in Spatial and Temporal Ozone Patterns Resulting from Emissions Reductions: Implications.
Examples of 1-Hour NO 2 and SO 2 Modeling William O’Sullivan Director, Division of Air Quality NJDEP June 14, 2011.
Paul Wishinski VT DEC Presentation for: MARAMA-NESCAUM-OTC Regional Haze Workshop August 2-3, 2000 Gorham, New Hampshire LYE BROOK WILDERNESS CLASS I AREA.
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.
Rice University Tropospheric Ozone Pollution Project (RU-TOPP) Gary A. Morris.
Department of the Environment Tad Aburn - Air Director, MDE June 21, AWMA Meeting - San Antonio, TX Complying With the NAAQS and Beyond -
Dependence of PM on Elevation Background and Rationale Influence of the Seasonal Variation in Mixing Heights on the PM Elevation Dependence Vertical Profile.
METO 637 Lesson 19. NO x emission inventory VOC Emissions.
Q. Name 3 factors that cause the reduction of hurricane intensity after it makes landfall. loss of warm moist air reduced temperatures greater.
1 Progress Report to MDE October 22, 2009 Dr. Konstantin Vinnikov, Acting State Climatologist for Maryland Prof. Russell Dickerson, Department of Atmospheric.
Air Masses and Weather Fronts
Air Pollution Outline Meteorological Factors Affecting Air Pollution
1 Progress Report to MDE June 7, 2010 Dr. Konstantin Vinnikov, Acting State Climatologist for Maryland Prof. Russell Dickerson, Department of Atmospheric.
OTAG Air Quality Analysis Workgroup Volume I: EXECUTIVE SUMMARY Dave Guinnup and Bob Collom, Workgroup co-chair “Telling the ozone story with data”
Department of the Environment The State Implementation Plan Process – Our Next Steps Brian Hug Division Chief, Air Quality Planning and Policy Division.
Department of the Environment What Will It Take? 2013 Power Plant Regulations Stakeholder Meeting - October 21, 2013 Meeting the New Ozone and Sulfur.
Department of the Environment A History of Power Plant Controls in Maryland What Did We Learn? – Where do We go Next? Part 1 – Background and Historical.
Ozone Season Summary 2014 Sunil Kumar MWAQC-TAC Meeting, COG September 9, Item #2.
CAPITA CAPITA PM and Ozone Analysis A. PM2.5 National Maps B. Visibility (PM2.5) trends C. Natural (out of EPA jurisdiction) Events D. US-Canada Ozone.
Colorado Plateau Sulfate Episode Worst 20% at 5 sites: INGA, BRCA, MEVE, WEMI & SAPE Best 20% at GICL, SACR, CHIR, SIAN, GUMO, TONT, and most California.
Maryland’s Innovative Measures State Implementation Plan 2004 EPA Air Innovations Conference Brian J. Hug – Chief, Air Quality Policy and Planning Division.
Regional Issues Facing Colorado and Other Western States WESTAR Spring Business Meeting Denver, Colorado March 30, 2010 Paul Tourangeau Director Colorado.
Research and Development to Meet Urban Weather and Climate Needs Dr. Richard D. Rosen NOAA Research September 23, 2004 Presentation at “Challenges in Urban.
AOSC 200 Lesson 14. Photochemical SMOG SMOG Chemistry.
Estimating local versus regional contributions to tropospheric ozone: An example case study for Las Vegas Mark Green and Dave DuBois Desert Research Institute.
Pollution Over the Red Sea: A Transboundary Air Quality Study Aiman Soleiman 1, Mahmoud Abu-Allaban 2, Menachem Luria 3, Bob Bornstein 4, Alan Gertler.
Air Pollution Transport and How It Affects New Hampshire A Report Prepared by the N.H. Department of Environmental Services May 18, 2004.
Travis D. Miller Department of Soil and Crop Sciences Texas AgriLife Extension Service The 2011 drought situation: July, 2011 Travis D. Miller Professor,
Martin O’Malley, Governor | Anthony G. Brown, Lt. Governor | Shari T. Wilson, Secretary AQ Cycles Re-examined: Shifting of the Bermuda High and Changes.
Montgomery County Department of Environmental Protection Montgomery County, MD Regional Wind Power Purchase Ann Elsen Energy Planner.
A Simplified Conceptual Model for the Ozone Transport Region OTC Modeling Committee Meeting Tad Aburn, MDE April 26, 2005 Where does our air pollution.
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.
Transboundary Air Pollution Plan of Islamic Republic of Iran
CMAQ APPLICATION TO OZONE POLLUTION IN THE PEARL RIVER DELTA OF CHINA Wei Zhou 1,2,Yuanghang Zhang 1,Xuesong Wang 1,Daniel Cohan 2 1.College of Environmental.
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,
The small Cornish village of Boscastle is not prone to regular annual flooding as many locations affected by extreme flooding events are. The village.
OTAG Air Quality Analysis Workgroup Volume I: EXECUTIVE SUMMARY Dave Guinnup and Bob Collom, Workgroup co-chair Telling the OTAG Ozone Story with Data.
August 1999PM Data Analysis Workbook: Characterizing PM23 Spatial Patterns Urban spatial patterns: explore PM concentrations in urban settings. Urban/Rural.
Why Are We Pushing for Aggressive Federal Rules to Reduce National/Regional NOx, SO2 and Hg Emissions? NACAA Board Meeting July 31 to August 2, 2010 PREPARED.
Ozone Transport that Impacts on Tribal Land: Case Study Stan Belone Salt River Pima-Maricopa Indian Community.
A Case Study of the 18 th January 2015 High-Impact Light Freezing Rain Event Across the Northern Mid-Atlantic Region Heather Sheffield Meteorologist Steven.
Martin O’Malley, Governor | Anthony G. Brown, Lt. Governor | Robert M. Summers, Ph.D., Secretary Solving the Ozone Transport Problem Tad Aburn, Air Director,
CALGRID Modeling Overview A First Look A Modeling Effort by the OTC Modeling Committee Presented by: Jeffrey Underhill, Ph.D. NHDES OTC/MANE-VU Annual.
August 1999PM Data Analysis Workbook: Characterizing PM23 Spatial Patterns Urban spatial patterns: explore PM concentrations in urban settings. Urban/Rural.
Eastern US Transport Climatology During Average, High and Low Ozone Days Bret A. Schichtel and Rudolf B. Husar Center for Air Pollution Impact and Trend.
Atmospheric Lifetime and the Range of PM2.5 Transport Background and Rationale Atmospheric Residence Time and Spatial Scales Residence Time Dependence.
Fire impacts – Natural event data exclusions/ozone monitoring Colleen Delaney, Utah Division of Air Quality March 11, 2004.
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.
1 Long Range Transport of Air Pollution Air pollution can travel hundreds of miles and cause multiple health and environmental problems on regional or.
A Basis for Control of BART Eligible Sources
A History of Power Plant Controls in Maryland What Did We Learn
The Turbulent Structure of the Urban Boundary Layer
The average PM2.5 mass concentration based on IMPROVE data available from September 2000 to December 2002 is 3.3 mg/m3 The highest occurrence of the 20%
Maryland's Air Quality: Nitrogen Reductions and the Healthy Air Act
Why Are We Pushing for More Federal Rules to Reduce Regional NOx and SO2? NACAA Meeting May 17, 2010.
Jenny L. Perry and Patrick M. Owens Department of Chemistry
Examples of 1-Hour NO2 and SO2 Modeling William O’Sullivan Director, Division of Air Quality NJDEP April 28, 2011.
DG Stakeholder Meeting - June 24, 2013
Presentation transcript:

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

Marylands Air Quality Ozone levels in Maryland are very high Fine particulate levels are high Air pollution contributes significantly to Bay pollution Regional haze and air toxics are also significant air pollution problems in Maryland

Major Theme Across Entire Program TRANSPORT

A Primer on Transport Transport 101- Where does Marylands poor air quality come from –Background on Marylands air quality –The role of transported pollution Transport 201 – The three types of transport –Short-range transport –Westerly transport –Low level night time jets

Nitrogen Deposition to the Chesapeake Bay

A Quick Primer on How Ground Level Ozone is Formed

Are Emissions Higher in Maryland? Source: U.S. EPA data tons per year States

So Where Does It Come From? Air pollution floating in from other states (called transport) is a significant contributor to our air pollution problems –Maryland – the meteorologically challenged state –MDE/UMCP Aircraft that measure incoming pollution –Models that predict state by state contributions

Classic Ozone Weather in the Mid-Atlantic H Maryland sees its worst air pollution during the summer when a Bermuda High sets up over the Carolinas

Power Plant Emissions H Very large power plant emissions concentrated along the Ohio River valley Air aloft circulates clockwise around the high

How Much Comes From Out of State? MDE works in partnership with the University of Maryland – College Park to measure and analyze pollution being transported into Maryland On our worst days we measure ozone at 110 parts per billion (ppb) floating into the state from the West –The 8-hour standard is 85 ppb

Who is Contributing to Marylands Ozone Problem? From EPAs modeling to support the 22 state regional NOx reduction program called the NOx SIP Call

Are Local or Regional Reductions Better? In Maryland, our technical analyses show that on our worst days –Local reductions are not very good at reducing local ozone. –In other areas, like Atlanta, local reductions seem to be much more effective On days where our ozone is more home grown local reductions are more important –Not our worst days, but we often see high ozone

Transport 201 The different types of transport The elevated ozone reservoir Short range transport Westerly transport Low level night time jets

Is It Just Power Plants or are There Other Types of Transport? Marylands location places us at the air pollution crossroads when if comes to transport. Air pollution floats to us from the west and the south. Sometimes the air pollution we transport to the north actually re-circulates back to us. Power plants, cars and area sources are all involved in the transport process

Three Types of Transport That Affect Maryland Short range –VA to MD to PA, etc. Long range (synoptic scale) –100s of miles –Generally from W or NW Low Level Night-time Jets –100s of miles –SW to NE along the Atlantic All types of transport collect in an elevated reservoir of ozone

The Elevated Ozone Reservoir Every bad ozone day, before any new ozone has been formed, a large reservoir of ozone sits above Maryland waiting to mix down. Ozone levels in the reservoir can routinely reach 80 to 100 ppb Early Morning Ozone Western Maryland Surface ozone is very low Ozone 2000 feet above the surface is very high

What Creates the Reservoir? At night the earth cools and a nocturnal inversion is created several hundred meters above the surface Ozone, created earlier in the day is trapped above the inversion and moved to the north by night-time jets. Ozone below the inversion drops to very low levels.

This hourly ozone graph for a summer day near Frederick, Maryland shows ozone concentrations reaching a minimum in the early morning hours. Ground Level Ozone at Night

Regional Scale Ozone In this case from July, 1999, the high elevation monitor at Methodist Hill in southern PA is above the nocturnal inversion. By late morning, mixing has brought all monitors to the common regional level.

Where Does the Reservoir Come From? The elevated ozone reservoir above Maryland is a complex mix of pollution that originated in the west (primarily power plants) and the south (cars, area sources and stationary sources)

Short Range Transport Central VA to DC DC to Baltimore Baltimore to PA Ground level winds from the southwest to the northeast Emissions from cars, area sources and stationary sources float to the northeast and add to high ozone levels downwind

Westerly Transport On Marylands worst ozone days westerly transport plays a significant role in creating high ozone.

Classic Ozone Weather in the Mid-Atlantic H Maryland sees its worst air pollution during the summer when a Bermuda High sets up over the Carolinas

Power Plant Emissions H Very large power plant emissions concentrated along the Ohio River valley Air aloft circulates clockwise around the high

Westerly Transport – What Does the Data Tell us About Its Origin? CORRELATES WITH HIGH AGED NOX * ITS OLD * CORRELATES WELL WITH SO2 * PROBABLY POWER PLANTS * DOES NOT CORRELATE WELL WITH CO * NOT CARS * HIGH OZONE ALOFT

Low Level Jet The Low Level Jet Night time transport that moves air from NC to MD, MD to NJ, etc. The Jet is funneled northward by the Appalachians on the west and the Atlantic on the east Wind speeds up to 40 miles per hour can move pollution hundreds of miles overnight.

Low Level Jet Recorded Above Fort Meade Maryland LLJ WHAT DOES THIS GRAPH TELL US? WIND SPEED AND DIRECTION ABOVE FT MEADE MD AUGUST PM TO 8AM. AUGUST PM TO 8AM.. AUGUST PM TO 9AM am. NOCTURNAL INVERSION UP TO ABOUT 1000 FEET. AUGUST 10 WINDS FROM THE SOUTHWEST AT ABOUT 25 to 30 MPH 1000 FEET ABOVE THE SURFACE AUGUST 11 WINDS FROM THE SOUTHWEST AT ABOUT 30 to 40 MPH 1000 FEET ABOVE THE SURFACE AUGUST 12 WINDS FROM THE SOUTHWEST AT ABOUT 30 to 40 MPH 1000 FEET ABOVE THE SURFACE 35 MPH FOR 6 HOURS IS ABOUT 200 MILES

Model Depiction of the Low Level Jet High Wind Speeds In Red 9:00 PM11:00 PM 01:00 AM 03:00 AM05:00 AM 07:00 AM

How Much Ozone May be in the Low Level Jet? Still analyzing this issue Theory and recent work by Penn State around Philadelphia (using laser technology called LIDAR) indicates that the low level jet can routinely carry 80 to 90 ppb ozone.

Take Home Messages Marylands air quality is significantly affected by transport from upwind areas to the west and the south On the worst ozone days well over half of the measured ozone in Maryland originates in upwind states Sources that transport pollution to Maryland include power plants, cars and area sources.

Thanks….. Brian Hug Division Chief, Planning and Policy Division