Health Effects of Air Pollution: Beyond the “Criteria” Pollutants Philip Bromberg MD 1 Ilona Jaspers PhD 1 Ken Sexton PhD 1 Harvey Jeffries PhD 1 W. Michael.

Slides:



Advertisements
Similar presentations
Measuring the Health Impacts of Air Pollution in Toronto and Hamilton Murray M. Finkelstein PhD MD Associate Professor, Department of Family Medicine and.
Advertisements

1. Components of Air pollution SMOG inc. Ozone Causes respiratory discomfort and inflames lungs. Formed in sunlight from VOC and NO 2. Sulphur dioxide.
Comparison of the Biological Effects of Sudbury Particulate Matter (SPaM) with Other Particulate Types: Acute and Chronic Studies Sarah M. White Stacey.
Ecology M. Saadatian Air Pollution 1.
Health Effects: Diesel Exhaust Maureen Edwards, MD, MPH Center for Maternal & Child Health MD Dept. Health & Mental Hygiene
Critical Issues of Exposure Assessment for Human Health Studies of Air Pollution Michelle L. Bell Yale University SAMSI September 15, 2009.
Improving Life, One Breath at a Time LUNG-USAwww.lunginfo.org.
1 PHOTOCHEMICAL SMOG Swagath Navin Manohar. 2 Contents 1.Smog 2.Physical Significance 3.Photochemical Smog 4.Topography & Meterology 5.Future Scope 6.Summary.
The Framework of Modeling SOA Formation from Toluene Oxidation Di Hu and Richard Kamens Department of Environmental Sciences and Engineering, University.
Part 5. Human Activities Chapter 14 Human Effects: Air Pollution and Heat Islands.
GASP–I can't breathe! How statistics can be used to study pollution control Peter Guttorp Statistics University of Washington.
Urban Transportation and PM Particulate Matter include small airborne particles known to correlate positively with increased morbidity and mortality. This.
IMPACTS OF CRITERIA AIR POLLUTANTS ON THE RESPIRATORY HEALTH OF CHILDREN John R. Balmes, MD UCSF.
Urban Air Pollution & Monitoring &
Air Pollution. What is air pollution? The presence of chemicals in the atmosphere in quantities and duration that are harmful to human health and the.
Daily EQ: What is the ozone layer, where do you find it, and why is it important?
OZONE ATMOSPHERIC POLLUTION Ozone in urban smog J (Hans) van Leeuwen.
One-Atmosphere Research Program for Urban Gaseous/Particulate Matter and Human Health Effects Studies School of Public Health School of Medicine University.
6. Atmospheric Photochemical Reactions
TCEQ/NUATRC Air Toxics Workshop: Session V – Human Health Effects Nathan Pechacek, M.S. Toxicology Section Texas Commission on Environmental Quality
Simple Chemical modeling of ozone sensitivity
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.
Ozone and Health Deborah M. Drechsler, Ph.D. Sierra Ozone Summit June 4, 2008.
Air Pollution Dr. R. B. Schultz. Introduction Air pollution Types Air pollution Types Sources of pollutants Sources of pollutants Pollution and weather.
Proposed Identification of Environmental Tobacco Smoke as a Toxic Air Contaminant Public Workshop Cal/EPA Headquarters Building Sierra Hearing Room Sacramento,
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.
Transportation-related Air Pollutants Health Effects and Risk Linda Tombras Smith, PhD Chief, Health and Exposure Assessment Branch Research Division October.
Air Pollution General. Definition Air pollution may be defined as the presence in the air (outdoor atmosphere) of one or more contaminants or combinations.
Air and Air Pollution. Key Concepts  Structure and composition of the atmosphere  Types and sources of outdoor air pollution  Types, formation, and.
PERCH Air Quality Study An Assessment of Particulate Matter, Ozone, and Air Toxics in Escambia and Santa Rosa Counties.
Module 9 Photochemistry.
June 12 &13, 2007 Mickey Leland National Urban Air Toxics Workshop II – Houston, Texas 1 Albuquerque, New Mexico Community Scale Ambient Air Monitoring.
U.S. EPA DISCLAIMER EPA strongly cautions that these study results should not be used to draw conclusions about local exposure concentrations or risk.
Urban Air Pollution Public and Environmental Health Concerns –Elevated levels of toxic compounds Regional and Global Impacts –Background Chemistry and.
Mark Camp, M.D., F.A.C.P., F.C.C.P. The Lung Center, Norman, OK James D. Jeffers, Chad Roller, Khosrow Namjou, Ph.D. Ekips Technologies, Inc., Norman,
5.7 URBAN AIR POLLUTION. Major Chemical Pollutants in Photochemical Smog: Sources and Environmental Effects Toxic ChemicalSourcesEnvironmental Effects.
Photochemical Smog Help~ Ha.. You guys deserve it…
Urban Air Pollution GISAT 112. Learning Objectives Regions of the atmosphere Amount, composition of air we breathe Names of selected air pollutants Health.
Air Pollution. 3/11/2014 Describe how we can reduce the amounts of CO2 in the atmosphere.
Air Toxics Monitoring in the Houston- Galveston Area David Brymer, Texas Commission on Environmental Quality.
Air Quality Assessment in Populated Area, Houston Focused on NOx & SO2 Eon S. Lee.
Talking About Air Toxics John D. Wilson Galveston-Houston Association for Smog Prevention
HRM Houston Regional Monitoring 1 Hazardous Air Pollutants Ambient Air Monitoring Data Review Air Toxics: What We Know, What We Don’t Know, and What We.
Secondary Organic Aerosols
Air Pollution What controls the level? –Amount of pollutants entering the air. –Amount of space into which the pollutants are dispersed. –Mechanisms that.
Ch.4.  Other (Atmospheric) Environmental Problems Due to Fossil Fuels Urban ozone Particulates in air pollution (Fly ash) Others in troposphere.
Unit 3 – Environmental Chemistry.  A pollutant is any material or energy that can cause harm to a living thing.  Pollution is a change to the environment.
Photochemical Smog Lecture-2.
In vivo imaging of ICAM-1 targeted nanoparticles in XPC and wild mice exposed to ambient air pollution in São Paulo, Brazil Nilmara Alves Post-doctoral.
Air Quality in Texas Birnur Guven Houston Advanced Research Center June 23, 2010 – Johnson Space Center.
NUATRC/TCEQ Air Toxics Workshop October Air Toxics Air Toxics: What We Know, What we Don’t Know, and What We Need to Know Human Health Effects –
W. T. Hutzell 1, G. Pouliot 2, and D. J. Luecken 1 1 Atmospheric Modeling Division, U. S. Environmental Protection Agency 2 Atmospheric Sciences Modeling.
Why Georgia Needs Gooder: Health Effects of O3 and PM2.5
Lecture-3. Primary air pollutants - Materials that when released pose health risks in their unmodified forms or those emitted directly from identifiable.
Oxidant Mechanisms in Response to Ambient Air Particles Beatriz González-Flecha Department of Environmental Health Harvard School of Public Health Boston,
Retrofitting Transit Buses to Reduce Air Emissions Kim Perrotta, Air Quality Coordinator, Ontario Public Health Association CUTA Conference 2003.
CHOOSE CLEAN AIR FOR CALIFORNIA RALPH JOHN DI LIBERO, MD 135 TH LACMA PRESIDENT.
AIR CLIMATE & ENERGY RESEARCH PROGRAM B U I L D I N G A S C I E N T I F I C F O U N D A T I O N F O R S O U N D E N V I R O N M.
Garfield County Air Quality Monitoring Network Cassie Archuleta Project Scientist Board of County Commissioners – Regular Meeting.
THE CHILDREN’S HEALTH STUDY May 6, 2002 Air Resources Board California Environmental Protection Agency.
Chapter 20 Air Pollution.
Air Pollution and Stratospheric Ozone Depletion
Clean Air Act Glossary.
Traffic Pollution and its impacts on our health?
16.3 Categories of Air Pollutants
Air Monitoring Trends in New Jersey
The airway epithelium nucleotide-binding domain and leucine-rich repeat protein 3 inflammasome is activated by urban particulate matter  Jeremy A. Hirota,
Barbara MacKinnon PhD New Brunswick Lung Association
Major Air Pollutants.
Environment, People, Prosperity: Toward A Balance We Can Live With
Presentation transcript:

Health Effects of Air Pollution: Beyond the “Criteria” Pollutants Philip Bromberg MD 1 Ilona Jaspers PhD 1 Ken Sexton PhD 1 Harvey Jeffries PhD 1 W. Michael Foster PhD 2 1 Univ. North Carolina 2 Duke University Air Toxics Workshop II Session 1 12 June 07 Mickey Leland Center Houston, TX

Introduction Ozone (O 3 ) –Produced in ambient air by photochemistry of NOx and hydrocarbons (primary emissions) –High reactivity -> ozonized reactive biological products in airways after inhalation –E.g., 4-OH nonenal, an unsaturated aldehyde with an acrolein motif (-CH=CH-CH=O).

Introduction (cont’d) Biologic effects in humans –Irritant (bronchial C fibers and A-delta fibers) –Reversible decrease in lung function –Acute airways inflammation (IL-8, IL-6, PGE2) –Increased epithelial permeability

Introduction (cont’d) Ozone as a surrogate –Other toxic species (oxy-organics) in ambient air –Some oxy-organics are recognized “air toxics” (e.g., HCHO, acetaldehyde, acrolein) –Others remain to be identified and characterized –Ozone itself may or may not be directly involved in their formation –Interaction of poorly volatile oxy-organics with ambient particulate matter

Is ozone responsible for all the health effects observed in human populations exposed to photochemical smog? –Yes, and –No!

Respiratory Hospital Admissions by Daily Maximum Ozone Level, Lagged One Day Ozone Concentration (ppm) Respiratory Admissions D-8a (Burnett et al, 1994)

In-Vitro Exposure Systems Interfaced to Environmental Irradiation Chambers Interfaced in-vitro gaseous exposure systems to these smog chambers, allowing A549 cells, an alveolar type II-like cell line, and primary human bronchial epithelial cells, grown on membranous support, to be exposed in real-time, directly to the gaseous photochemical mixture or ”control” mixture and analyzed for cytotoxicity and cytokine gene expression. ?? Attain goal of whole natural gas-phase exposure sample All products, both known and unknown, produce exposure; product yields and resulting mixtures are natural (realistic exposure ratios)

Cytotoxicity induced by the photochemical transformation of HAPS

Inflammatory gene expression induced by the photochemical transformation of HAPS : Methanol, Isoprene (ISO), 1,3-Butadiene (BD)

Uncertainties in Estimating Exposure and Risk in Atmospheric Aging Effects Many reaction rates and product yields are uncertain Many reaction products are detected but not identified Many reaction products are unknown or difficult to detect or quantify How can we estimate exposure and risk given these uncertainties and unknowns ?

Resuspended DP from Diesel-Urban VOC Mixtures: Effect of Photochemical Aging Create/Obtain DEP in rooftop smog chamberat UNC Obtain C57BL/6J mice at Duke Day 1- Instill DEPs(6 mice per group) Dark Fresh 28.8µg/ 50µL Photochemically Aged 30.5µg/ 50µL PBS (phosphate buffered saline) 50µL Dark Fresh 44.4µg/ 50µL Dark Aged 39.0µg/ 50µL PBS (phosphate buffered saline) 50µL Day 4- Repeat Doses in mice Day 7- Repeat Doses in mice Day 8- Euthanize for lavage/tissue collection or Perform PFTs

* * * * * = p<0.05 * * * *

Fresh DEP Aged DEP PBS Control Hematoxylin and Eosin (H and E) Staining- stains nucleic acids and intracellular and extracellular proteins HISTOLOGY

Aged DEP instilled mice showed GREATER airway hyperresponsiveness compared to the ozone exposed mice. * * * (p=.079)

Resuspended DP from Diesel- Urban VOC Mixtures: Effect of Photochemical Aging

Summary/Conclusions “Air Toxics” and “Criteria Pollutants” interact. They should not be treated as totally distinct categories. Photochemistry transforms many (not all) volatile organic compounds into less volatile oxy-organics that are toxic in their own right and may interact with PM.

Summary/Conclusions (cont’d) Photochemical smog clearly causes adverse respiratory health effects, notably in asthmatics. Ozone is toxic on its own, but may also be a surrogate for toxic oxy- organic species. Houston is positioned to lead in this area of air pollution research and application. A multi-disciplinary team approach is required to obtain the needed information.

Summary/Conclusions (cont’d) Such knowledge is essential for –Targeted air quality monitoring –Cost-effective measures to control key emissions –Reasonable expectation that these measures will improve public health.

Student Investigators Melanie Doyle, PhD (2006) –Currently at Lovelace Resp. Res. Inst. Kim deBruijne MS (2006) –Currently a PhD candidate at U.N.C. Seth Ebersviller (grad. student) –Currently a PhD candidate at U.N.C.