L l AN ASSESMENT OF THE POTENTIAL FOR CO-EXPOSURE TO ALLERGENIC POLLEN AND AIR POLLUTION IN COPENHAGEN, DENMARK Pia Viuf Ørby 1, Robert Peel 2, Carsten.

Slides:



Advertisements
Similar presentations
1 The Air Quality Health Index & 20/20 The Way to Clean Air Protecting Your Health and Reducing Air Pollution.
Advertisements

Measuring the Health Impacts of Air Pollution in Toronto and Hamilton Murray M. Finkelstein PhD MD Associate Professor, Department of Family Medicine and.
Climate change and lung health PJ Helms European Respiratory Society University of Aberdeen Scotland UK.
DIURNAL PATTERN OF SUBMICRON AEROSOL SIZE/MASS DISTRIBUTIONS IN URBAN ATMOSPHERE, PRAGUE WINTER 2004/2005 J. HOVORKA 1, M.BRANIŠ 1, J. SCHWARZ 2
ACCENT-plus Symposium, Urbino 2013 The effect of climate and climate change on ammonia emissions in Europe Camilla Geels 1 and Carsten Ambelas Skjøth 2.
Fighting the Great Challenges in Large-scale Environmental Modelling I. Dimov n Great challenges in environmental modelling n Impact of climatic changes.
Update: National Ambient Air Quality Standards Association of California Airports September 15, 2010 Phil DeVita.
Direct effects of climate change on plants in Hungary Eszter Erdei, J. Bobvos**, T. Hardy*, E. Jozsa*, A. Paldy* * Natl. Institute of Environmental Health,
The concentration of malondialdehyde in exhaled breath is influenced by air pollution exposure during physical activity in adolescents Kaytna Thaker Department.
TRENDS IN HOSPITALIZATION RATES FROM ASTHMA IN CHILDREN AND ADOLESCENTS IN POLAND Krystyna Szafraniec 1, Wieslaw Jedrychowski 1, Bogdan Wojtyniak 2 and.
Critical Issues of Exposure Assessment for Human Health Studies of Air Pollution Michelle L. Bell Yale University SAMSI September 15, 2009.
Correction of Particulate Matter Concentrations to Reference Temperature and Pressure Conditions Stefan R. Falke and Rudolf B. Husar Center for Air Pollution.
IMPACTS OF CRITERIA AIR POLLUTANTS ON THE RESPIRATORY HEALTH OF CHILDREN John R. Balmes, MD UCSF.
UK Air Quality Indicators Janet Dixon Air and Environment Quality Division, Department of Environment, food and Rural Affairs, UK.
1 The Air Quality Health Index & 20/20 The Way to Clean Air Protecting Your Health and Reducing Air Pollution.
THE ADVANTAGES OF ROAD-SIDE AIR POLLUTION DATA FOR IDENTIFYING PRIORITY IN TRAFFIC MANAGEMENT AND URBAN HOTSPOT MONITORING Driejana 1 *, Harmein Rahman.
Ozone NAAQS – Issues with the Science Presented by: Lucy Fraiser Zephyr Environmental Corporation February 5, 2015 Air & Waste Management Association Hot.
The Most Important Global Public Health Issue: AIR POLLUTION By: Maria Mueller Margaret Ndetti Dr. Butler Date: November 19, 2007.
Review of the Potential Health Impacts of Climate Change-Related Effects on Air Quality Kristie L. Ebi, Ph.D., MPH Exponent Climate Science.
Air Resources Board California Environmental Protection Agency Air Quality Effects of Trap-Related Emissions John DaMassa April 18, 2002 Originally Presented.
Science Investigation Discussion of Results to Date & Future Work Red Deer Particulate Matter Information Session Maxwell Mazur
Observations The collection of slope values were plotted against time and box plots show the distribution for each of the six daily trips of the vessel.
1 Scripps Inst. of Oceanography University of California at San Diego Oakland, California, October 18, 2013 V. Ramanathan, University of California, San.
1 Communicating air quality trade-offs. Module 6. Communicating Air Quality to the Public in the Mid-Atlantic United States.
Facts for Health Professionals. Health Impacts: General Symptoms/ Health Impacts Causes Sources of pollutants Links 54% increased risk of stroke Particulate.
Health Effects of Air Pollution
Accessing Air Quality Lessons on MY NASA DATA
A METHOD TO ASSESS COMPETING RISKS ASSOCIATED WITH PEDESTRIAN-ORIENTED ENVIRONMENTS Audrey de Nazelle and Douglas Crawford-Brown Department of Environmental.
The Negative Impact of Air pollution on Respiratory Health Dr Des Murphy Consultant Respiratory Physician CUH.
Asthma is the most prevalent chronic illness among children and adolescents, reported in 1 in 10 children. 1 With an estimated 10.5 million missed days.
Exposure Assessment for Health Effect Studies: Insights from Air Pollution Epidemiology Lianne Sheppard University of Washington Special thanks to Sun-Young.
Opening Remarks -- Ozone and Particles: Policy and Science Recent Developments & Controversial Issues GERMAN-US WORKSHOP October 9, 2002 G. Foley *US EPA.
The Environment and You: Find Air Quality Information Helena VonVille, MLS Library Directory University of Texas School of Public Health at Houston Harris.
Voivodeship Inspectorate of Environmental Protection in Szczecin ASSESSMENT OF AIR QUALITY IN SZCZECIN AGGLOMERATION.
Montserrat Fuentes Statistics Department NCSU Research directions in climate change SAMSI workshop, September 14, 2009.
AMGI/EURASAP workshop, Zagreb 25 May 2007 Nenad Kezele, Ruđer Bošković Institute, Bijenička 54, Zagreb, Croatia Effect of O 3 and PM10 on mortality increase.
Air pollution in Stuttgart ? NO 2 O3O3 PM 10. Stuttgart.
Air Quality Index How Healthy is the Air You Breathe?
Konstantina Dimakopoulou, Evangelia Samoli, Rob Beelen, Massimo Stafoggia, Zorana Jovanovic Andersen,Barbara Hoffmann etc. Air Pollution and Nonmalignant.
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:
Air Pollution, Cycling, and Health Emilia Hanna Air Pollution Campaigner Friends of the Earth Scotland Presentation to Spokes Public Meeting 13 June 2016.
Correlations between DTT Activity and PM Constituents Wing Tuet April
Hamilton Air Quality Trends Denis Corr Department of Engineering Physics McMaster University Lidar Workshop April 25, 2007.
By Cesar E. Lebron. Bronx County has some of the highest rates of asthma in the United States. Rates of death from asthma in the Bronx are about three.
Satellite Data for Health & Air Quality Applications
N Engl J Med Jun 29;376(26): doi: 10
of Temperature in the San Francisco Bay Area
Clinical Application of Nasal Filters: An Observational Study on the Usability of Nasal Filters in Managing Seasonal Allergic Rhinitis  Peter Kenney,
The Human Health Co-Benefits of Fossil Fuel Emissions Reductions for Climate Change Mitigation George D. Thurston, ScD. Professor NYU School of Medicine.
EXPOSURE OF CHILDREN TO ULTRAFINE PARTICLES AROUND AN URBAN INTERSECTION S Kaur, M J Nieuwenhuijsen & R Colvile Environmental Processes & Systems Research.
EUROEPI2010 -EPIDEMIOLOGY AND PUBLIC HELTH IN AN EVOLVING EUROPE
Vitamin D insufficiency, preterm delivery and preeclampsia in women with type 1 diabetes – an observational study MARIANNE VESTGAARD1,2,3 , ANNA L. SECHER1,2.
Traffic Pollution and its impacts on our health?
Short seasons and nightly atmospheric circulation of allergenic pollen in Augsburg, Germany: is it really good news? Dr. A. Damialis.
Exposure to Air Pollution James Tate and Paul Seakins
of Temperature in the San Francisco Bay Area
Quantification of the Natural Variation in Traffic Flow
Global Pollen Trends: Effects of Temperature and Precipitation
Clinical Application of Nasal Filters: An Observational Study on the Usability of Nasal Filters in Managing Seasonal Allergic Rhinitis  Peter Kenney,
Visualization and Analysis of Air Pollution in US East Coast Cities
Updating the science on health assessment
Barbara MacKinnon PhD New Brunswick Lung Association
Bart Ostro, Chief Air Pollution Epidemiology Unit
Forest fires and air pollution in Portugal
Contributions to total changes in emissions of ozone precursors
WORK OF THE UNITED KINGDOM AIR QUALITY EXPERT GROUP (AQEG)
Air Quality In Cambridge
Table 2. Results of 24-hour air monitoring sampling in risk area
Air Quality and Health Dr Liz Robin Director of Public Health
Dental Office Hours Air Quality By Olivia Potthoff and Abigail Shaffer
Presentation transcript:

l l AN ASSESMENT OF THE POTENTIAL FOR CO-EXPOSURE TO ALLERGENIC POLLEN AND AIR POLLUTION IN COPENHAGEN, DENMARK Pia Viuf Ørby 1, Robert Peel 2, Carsten Ambelas Skjøth 3, Vivi Schlünssen 1, Jakob Bønløkke 1, Thomas Ellermann 2, Andreas Brændholt 5, Torben Sigsgaard 1, Ole Hertel 2,4 1 Unit of Environmental and Occupational Medicine (DEOM), Department of Public Health, Aarhus University, 2 Department for Environmental Science, Aarhus University, 3 National Pollen and Aerobiology Research Unit, University of Worcester, 4 Department for Environmental, Social and Spatial Change (ENSPAC), Roskilde University. 5 Asthma-Allergy Association Denmark. Background. Co-exposure to air pollutants and allergenic pollen can exacerbate allergic airway diseases. Charts above. Yearly plots of 11-day running mean for for PM (a) and the gasses O 3, NO 2 and SO 2 (b) for both roadside (Jagtvej or HCAB) and urban background (HCØ). Typical birch and grass pollen seasons based on the period are shaded grey. Charts, left. Diurnal charts of the average patterns of (a) birch pollen and (b) grass pollen on peak and non-peak pollen days. Peak pollen days are days with concentrations above 50 grains m -3 for grass pollen and 100 grains -3 for birch. Charts above. Diurnal charts of the average patterns of pollutants with standard error of the means; (a) PM 2.5 at roadside (HCAB) and rooftop (HCØ), (b) PM 10 at roadside (HCAB) and rooftop (HCØ), (c) O 3 and NO 2 at HCØ rooftop station, (d) NO 2 at roadside (Jagtvej) roadside station, (e) O 3 at Jagtvej roadside station, (f) SO 2 at HCAB roadside station. Contact: Pia Viuf Ørby, Birch pollen 25 um Grass pollen 35 um Aim. Patterns in pollutant and pollen concentrations at which co-exposure may be a particular risk with respect to adjuvant health effects were analysed by: - Comparing the yearly pattern of the concentrations of pollutants with the timing of pollen seasons. -Comparing the average diurnal pattern of concentrations of pollen and pollutants on days with (a) high pollen concentrations and for (b) the remaining part of the pollen season. This is pursued in order to establish if there are typical patterns of concurrently high concentrations, which could affect the guidance to the allergic and asthmatic public. Methods. We examined yearly variation and diurnal patterns of pollutants on days with high pollen levels, and also for the remaining part of the pollen season, for the following: grass and birch pollen, sulphur dioxide (SO 2 ), ozone (O 3 ), nitrogen dioxide (NO 2 ) and particulate matter (PM) in the period Results. O 3 concentrations were increased on days with peak pollen concentrations. High O 3 concentrations coincide both seasonally and diurnally with high pollen counts, potentially leading to clinically relevant simultaneous co-exposure. NO 2 and SO 2 peaks did not coincide with peaks in pollen concentrations, and were well below potential thresholds for adjuvant effects to the allergic reaction. Neither diurnal nor seasonal peaks in PM coincide with pollen peaks, however daily average PM concentrations were higher on peak pollen days than on non-peak days. Conclusions. This study indicates that when considering co-exposure effects from pollen and pollutants, O 3 appears to be the most relevant pollutant to further examine for clinical effects of simultaneous co- exposures. Results shown are under review for publication in the journal Urban Climate. Co-exposure to ozone and allergen After one hour of exposure to 120 ppb of O 3, Molfino et al. [1991] found that only half the allergen dose was needed to provoke a 20% drop in FEV1 compared to exposure to clean air. The O 3 concentrations observed in this study are lower than these, but their effect are expected to be of clinical relevance [Van Bree et al., 1995]. References. Molfino, N. A., Wright, S. C., Katz, I., Tarlo, S., Silverman, F., McClean, P. A., Slutsky, A. S., Zamel, N., Szalai, J. P., and Raizenne, M., Effect of low concentrations of ozone on inhaled allergen responses in asthmatic subjects, The Lancet 338 (1991) , Van Bree, L., Marra, M., Van Scheindelen, H. J., Fischer, P. H., De Loos, S., Buringh, E., and Rombout, P. J. A., Dose-effect models for ozone, Toxicol. Lett. Volumes (1995)