Pacific 2001 – Synthesis of Findings and Policy Implications Roxanne Vingarzan Pacific and Yukon Region.

Slides:



Advertisements
Similar presentations
1 Policies for Addressing PM2.5 Precursor Emissions Rich Damberg EPA Office of Air Quality Planning and Standards June 20, 2007.
Advertisements

Atmospheric Aerosol From the Source to the Receptor Insights from the Pittsburgh Supersite Spyros Pandis, Allen Robinson, and Cliff Davidson Department.
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.
Development of a Secondary Organic Aerosol Formation Mechanism: Comparison with Smog Chamber Experiments and Atmospheric Measurements Luis Olcese, Joyce.
Control of Nitrogen Oxides Dr. Wesam Al Madhoun. Specific sources of NO x Combustion sources Automobiles Boilers Incinerators High-temperature industrial.
AIR POLLUTION IN THE US : Ozone and fine particulate matter (PM 2.5 ) are the two main pollutants 75 ppb (8-h average) 15  g m -3 (1-y av.)
QUESTIONS 1.Is hexane more or less reactive with OH than propane? 2.Is pentene or isoprene more reactive with OH?
P. D. Hien, V. T. Bac, N. T. H. Thinh Vietnam Atomic Energy Commission.
Introduction & Outline Particulate Measurement 1) PM10 – Particulate Matter < 10 microns 2) PM2.5 – Particulate Matter < 2.5 microns - Measured with different.
Evaluation of Secondary Organic Aerosols in Atlanta
1 Non-linear effects in modelling PM 10 and PM 2,5 contributions from anthropogenic sources Clemens Mensink, Felix Deutsch, Jean Vankerkom and Liliane.
Air Quality Impacts from Prescribed Burning Karsten Baumann, PhD. Polly Gustafson.
Discussion Space Research Centre. Urbanization and Industrialization: in 2008, more than half of humans live in cities UN Population Report 2007.
METO 637 Lesson 15. Polar meteorology In the winter months the poles are in perpetual darkness. This causes extremely cold temperatures in the stratosphere.
Investigating the Sources of Organic Carbon Aerosol in the Atmosphere Colette L. Heald NOAA Climate and Global Change Postdoctoral Fellow University of.
University of Leicester CityZen Contributions
Chemical composition of aerosols Composition of tropospheric aerosols is not uniform. It varies with particle size and source of particles: Ultrafine particles.
Emissions of Volatile Organic Compounds by Plants Carbon Metabolism and Atmospheric Chemistry Kolby Jardine Amazon-PIRE Field Course June 2010.
WRAP Status + Fire Emissions Inventory Protocol for Regional Air Quality Analysis and Planning Support in the WRAP regionWRAP Tom Moore WRAP/Western Governors’
J. Zhou 1, X. Zhu 1, T. Wang 1, and X. Zhang 2 J. Zhou 1, X. Zhu 1, T. Wang 1, and X. Zhang 2 1 College of Resources and Information Tech., China University.
NATURAL AND TRANSBOUNDARY INFLUENCES ON PARTICULATE MATTER IN THE UNITED STATES: IMPLICATIONS FOR THE EPA REGIONAL HAZE RULE Rokjin J. Park ACCESS VII,
Simulation of European emissions impacts on particulate matter concentrations in 2010 using Models-3 Rob Lennard, Steve Griffiths and Paul Sutton (RWE.
QUESTIONS 1.If CO emission to the atmosphere were to double, would you expect CO concentrations to (a) double, (b) less than double, (c) more than double?
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.
Organics in the Mix during SAPUSS M. Dall´Osto and the SAPUSS team CSIC, Barcelona, Spain
APES Get out lab – keep at table. SMOG Ch. 18 Smog Localized air pollution in urban areas, mixture of pollutants that form with interaction with sunlight.
Air Quality, Atmospheric Deposition, and Lake Tahoe October 15, 2003 Western Regional Pollution Prevention Network Grannlibakken, Lake Tahoe Jim Pederson.
Urban Air Pollution IB syllabus: AP syllabus Ch 17, 18.
Results of Ambient Air Analyses in Support of Transport Rule Presentation for RPO Workshop November 2003.
FROM AIR POLLUTION TO GLOBAL CHANGE AND BACK: Towards an integrated international policy for air pollution and climate change Daniel J. Jacob Harvard University.
Evolving Understanding of Pollutant Transport from Asia to North America Richard (Tony) VanCuren Research Division, California Air Resources Board Department.
School of something FACULTY OF OTHER 1 Lecture 2: Aerosol sources and sinks Ken Carslaw.
Contribution from Natural Sources of Aerosol Particles to PM in Canada Sunling Gong Scientific Team: Tianliang Zhao, David Lavoue, Richard Leaitch,
Tore Flatlandsmo Berglen EACE workshop June 2007 Air quality, ozone and aerosols in Asia. A model study Tore Flatlandsmo Berglen 1,2, Terje K. Berntsen.
Properties of Particulate Matter Physical, Chemical and Optical Properties Size Range of Particulate Matter Mass Distribution of PM vs. Size: PM10, PM2.5.
What Causes Air Pollution /08. Air 78% Nitrogen 20 % Oxygen Carbon Dioxide, Argon and water vapor.
Air Pollution Anti-Lecture
Atmosphere and Air Pollution Chapter 18. Quick Recap.
U.S.-Canada Air Quality Agreement: Transboundary PM Science Assessment Report to the Air Quality Committee June, 2004.
Online measurements of chemical composition and size distribution of submicron aerosol particles in east Baltic region Inga Rimšelytė Institute of Physics.
PM Formation in the Atmosphere Primary and Secondary PM Sulfate Formation in the Atmosphere SO4 Formation in Clouds Season SO2-SO4 Transformation rate.
1.
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.
UNECE-CLRTAP and EMEP Task Force on Integrated Assessment Modelling 26th session, Brussels, May 2001 Integrating the environmental effects of Particulate.
Regional Air Quality Modeling Results for Elemental and Organic Carbon John Vimont, National Park Service WRAP Fire, Carbon, and Dust Workshop Sacramento,
Southeast US air chemistry: directions for future SEAC 4 RS analyses Tropospheric Chemistry Breakout Group DRIVING QUESTION: How do biogenic and anthropogenic.
QUESTIONS 1.Is hexane more or less reactive with OH than propane? 2.Is pentene or isoprene more reactive with OH? 3.Using the EKMA diagram (the ozone isopleth.
November Siebert Ground Level Ozone1 PHOTOCHEMICAL SMOG & OZONE.
August 1999PM Data Analysis Workbook: Characterizing PM1 Characterizing Ambient PM Concentrations and Processes What are the temporal, spatial, chemical,
Georgia Institute of Technology SUPPORTING INTEX THROUGH INTEGRATED ANALYSIS OF SATELLITE AND SUB-ORBITAL MEASUREMENTS WITH GLOBAL AND REGIONAL 3-D MODELS:
MILAGRO Science Workshop -- October 2006 Summary of preliminary discussions on near-, mid-, and far-field chemistry W. Brune reporting Preliminary Findings.
Breakout Session 1 Air Quality Jack Fishman, Randy Kawa August 18.
Aerosol Pattern over Southern North America Tropospheric Aerosols: Science and Decisions in an International Community A NARSTO Technical Symposium on.
Atmospheric Lifetime and the Range of PM2.5 Transport Background and Rationale Atmospheric Residence Time and Spatial Scales Residence Time Dependence.
BACKGROUND AEROSOL IN THE UNITED STATES: NATURAL SOURCES AND TRANSBOUNDARY POLLUTION Daniel J. Jacob and Rokjin J. Park with support from EPRI, EPA/OAQPS.
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.
Properties of Particulate Matter
OsloCTM2  3D global chemical transport model  Standard tropospheric chemistry/stratospheric chemistry or both. Gas phase chemistry + essential heteorogenous.
Sunil Kumar TAC, COG July 9, 2007
Background to Atmospheric Pollution
Dr. Tanveer Iqbal Associate Professor,
Characteristics of Urban Ozone Formation During CAREBEIJING-2007 Experiment Zhen Liu 04/21/09.
Nitrogen Deposition: Measurement Techniques and Field Studies
Major Air Pollutants: Part 2
Three policy scenarios for CAFE
Continuous measurement of airborne particles and gases
Steve Griffiths, Rob Lennard and Paul Sutton* (*RWE npower)
U.S. Perspective on Particulate Matter and Ozone
Title Why do we underestimate Elemental Carbon in PM?
RECEPTOR MODELLING OF AIRBORNE PARTICULATE MATTER
Presentation transcript:

Pacific 2001 – Synthesis of Findings and Policy Implications Roxanne Vingarzan Pacific and Yukon Region

Pacific 2001 Study Previous large scale studies in the FV addressed ozone and visibility issues but a knowledge gap remained concerning fine PM Policy Relevant Questions 11 policy-relevant questions were identified in order to provide guidance with policy setting and air quality management in the region 11 policy-relevant questions were identified in order to provide guidance with policy setting and air quality management in the region Subject areas:  Aerosol Distribution & Transport  Particle Chemistry & Spatial Patterns  Particle Formation and Growth  Particle Events - causes  Sources  Addressing fine PM

Contributions Synthesis is based on a review of 20 papers 14 papers published in first special issue of AE 14 papers published in first special issue of AE 6 papers submitted for the second special issue 6 papers submitted for the second special issue Contribution of a large number of authors AQRB, Downsview AQRB, Downsview EC, PYR EC, PYR 9 Canadian universities 9 Canadian universities 3 US universities 3 US universities 1 UK universities 1 UK universities

Aerosol Distribution Night Concentrated aerosols in the tributary valleys Afternoon Concentrated aerosols in the eastern part of the LFV

WISE EFFECT WISE Wake Induced Stagnation Effect Build-up of pollutants over the Gulf & San Juan islands area High PM levels over the Strait of Georgia afternoon of August 26

Upslope flow of aerosol during the night Polluted layers were occasionally, entrained into clean air masses at the surface by the PBL. Polluted layers were occasionally, entrained into clean air masses at the surface by the PBL. PBL Studies PBL as found to be suppressed in height and occur several hours earlier during sea breeze conditions. Above ground aerosol layers at Harrison Lk. Above ground aerosol layers at Harrison Lk. Transport Mechanisms From Strawbridge and Snyder, 2004

Particle Chemistry - Inorganics From Pryor et al. 2004

Nitrate Chemistry Daytime Fine mode dominated by ammonium sulphate Coarse mode dominated by NaNO3 Cl- ion depletion from reaction of HNO3 with sea salt particles Nighttime Fine mode nitrate production from NO3-N2O5-HNO3 pathway Fine mode ammonium nitrate occurred almost always during the night. Sumas From, McLaren et al. 2004

The Ammonium Ion & Fine PM Ammonium ion excess What is the excess ammonium bound to?

Particle Chemistry - Organics Organic carbon was found to comprise approximately half of the particle composition Organic carbon was found to comprise approximately half of the particle composition A broad suite of organic substances were detected, including alkanes, aromatics and various oxidized hydrocarbons including fatty acids A broad suite of organic substances were detected, including alkanes, aromatics and various oxidized hydrocarbons including fatty acids Both anthropogenic and biogenic hydrocarbons were found to be photochemically reactive and contribute to SOA and ozone formation Both anthropogenic and biogenic hydrocarbons were found to be photochemically reactive and contribute to SOA and ozone formation Isoprenes and monoterpenes were the dominant biogenic hydrocarbons detected - their presence at all sites indicated the broad influence of biogenic organics throughout the FV Isoprenes and monoterpenes were the dominant biogenic hydrocarbons detected - their presence at all sites indicated the broad influence of biogenic organics throughout the FV

Particle Events Sulphate growth events were associated with photochemical production from advected SO2 from industrial sources in north-west Washington state. Sulphate growth events were associated with photochemical production from advected SO2 from industrial sources in north-west Washington state. Fine particle nitrate events were associated with advection of HNO3 from the urban core into the eastern FV reacting with local sources of ammonia. Fine particle nitrate events were associated with advection of HNO3 from the urban core into the eastern FV reacting with local sources of ammonia. Organic particle growth events were associated with stagnant conditions and advection of air over urban Vancouver. Organic particle growth events were associated with stagnant conditions and advection of air over urban Vancouver.

Sources - Highlights Primary sulphate in the FV is consistent with gasoline, diesel & gas combustion. Primary sulphate in the FV is consistent with gasoline, diesel & gas combustion. Approximately 30% of the sulphate in PM2.5 aerosols estimated to be derived from the oxidation of DMS. Approximately 30% of the sulphate in PM2.5 aerosols estimated to be derived from the oxidation of DMS. Organic aerosols were found to have significant contributions from terrestrial (plant material) sources during the summer months and from fossil fuel sources during the spring months. Organic aerosols were found to have significant contributions from terrestrial (plant material) sources during the summer months and from fossil fuel sources during the spring months. Hydrocarbon species indicated contributions of light and heavy-duty (diesel) traffic, meat cooking & biogenic sources. Hydrocarbon species indicated contributions of light and heavy-duty (diesel) traffic, meat cooking & biogenic sources. Biomass burning generally had a small but measurable impact on the composition of ambient aerosols in the FV. Biomass burning generally had a small but measurable impact on the composition of ambient aerosols in the FV.

Spatial Patterns Slocan  emission controlled regime  PM dominated by organics, both anthropogenic and biogenic  mobile sector emissions - gasoline and diesel combustion and fugitive emissions of petroleum fuels.  Biogenic organics important Langley  formation controlled regime  PM dominated by inorganics  Sulphate levels highest due to the influence of advected SO2 from oil refineries in north- west Washington state.  Elevated ammonia and biomass burning markers reflected the influence of agricultural sources. Sumas  Mixed emission/formation regime dominated by urban, agricultural and biogenic sources.  Fine mode nitrate important  The chemistry was most variable Golden Ears  PM dominated by biogenic organics  chemistry impacted by anthropogenic sources due to upslope flow  biogenically derived SOAs were transported into the FV by downslope flow.

Policy Implications – Addressing Fine PM in the FV Hypotheses for emission scenario modelling Ammonia Emissions  Ammonia was found not to be a limiting species  Limited ammonia reductions are not expected to offer a significant improvement in reducing fine PM levels but large reductions may be more effective  Reductions may result in secondary negative secondary effects, such as changes to the acidity of ambient aerosols and of atmospheric deposition SOx Emissons  Sulphate was a limiting species  SOx reductions may aid in partially reducing fine PM, however only if accompanied by NOx reductions (NH4NO3)  Contributions from biogenic sulphate during spring/summer may limit success

Policy Implications - continued NOx Emissions  Nitrate was a limiting substance  NOx reductions are expected to reduce NH4NO3 production in the eastern FV (esp. in wet season).  Reductions in NOx in the absence of VOC reductions may result in an increase in SOAs in urban areas (increase in oxidants) VOC Emissions  VOC reductions may provide some benefits to air quality  Benefits would be limited by the biogenic contribution to fine PM.  Targeting VOC reductions in the absence of NOx reductions may result in an increase nitric acid in NOx rich areas. Concurrent Emission Reductions in ammonia, SOx, NOx and VOC emissions may be required to reduce fine PM

PAC2001 Policy Relevant Findings Summary Identified mechanisms of aerosol transport: seabreeze-landbreeze flows, upslope-downslope flows and north-south valley flows Identified mechanisms of aerosol transport: seabreeze-landbreeze flows, upslope-downslope flows and north-south valley flows Identified areas of enhanced aerosol concentrations: eastern FV, north-south tributary valleys & the WISE zone Identified areas of enhanced aerosol concentrations: eastern FV, north-south tributary valleys & the WISE zone Confirmed the importance of organic carbon and biogenic organics in fine PM Confirmed the importance of organic carbon and biogenic organics in fine PM Characterized the chemistry of coarse & fine mode PM Characterized the chemistry of coarse & fine mode PM Identified both anthropogenic and biogenic sources contributing to secondary organic aerosol formation Identified both anthropogenic and biogenic sources contributing to secondary organic aerosol formation Identified geographical patterns in emission regimes, PM composition and aerosol processing Identified geographical patterns in emission regimes, PM composition and aerosol processing Provided hypotheses for testing out emission scenarios aimed at reducing fine PM Provided hypotheses for testing out emission scenarios aimed at reducing fine PM