Air Quality and Your Health Susan Lyon Stone Clean Air Partners August 29, 2006 [email protected].
Download ReportTranscript Air Quality and Your Health Susan Lyon Stone Clean Air Partners August 29, 2006 [email protected].
Air Quality and Your Health Susan Lyon Stone Clean Air Partners August 29, 2006 [email protected] Human Lung • Air conducting – Trachea – Bronchi – Bronchioles • Gas exchange – Respiratory bronchioles – Alveoli Ozone Irritates Airways • Symptoms – Cough – Sore or scratchy throat – Pain with deep breath – Fatigue • Rapid onset • Similar symptoms - people with and without asthma FEV1, % CHANGE Ozone Reduces Lung Function 0 -20 -40 -60 BASELINE M-10 2HR 4HR M-1c Ozone Causes Inflammation • Ozone reacts completely in surface layer - forms reactive oxygen molecules • Influx of white blood cells • Damages cells that line the airways • Effect is greater 24 hours after exposure • Increases airway reactivity • Concern about repeated exposures – permanent structural changes Respiratory Admissions Respiratory Hospital Admissions by Daily Maximum Ozone Level, Lagged (Burnett et al, 1994) One Day D-8a 114 112 110 108 106 104 102 .01 .02 .03 .04 .05 .06 .07 .08 .09 .1 Ozone concentration (ppm) California Children’s Health Study CHS: School Absences • 20 ppb increase in O3 associated with an 83% increase in school absences for acute respiratory disease (Gilliland et al., 2001) • Large economic impact of pollution-related school absences (Hall and Lurmann, 2003) CHS: Ozone and New-onset Asthma McConnell at al., 2002 New Evidence from Current Review of Ozone Standard • Physiological bases of increased sensitivity of people with asthma – Larger decreases lung function – Increased occurrence and duration nonspecific airway responsiveness – Increased airway responsiveness to allergens – Increased inflammatory responses New Evidence from Current Review of Ozone Standard • • • • Hospital admissions Emergency room visits School absences Increased symptoms and medication use in asthmatic children New Evidence from Current Review of Ozone Standard - Mortality • Study done in Vancouver, BC with statistically significant results has 98 and 99 percentile values below 0.06 ppm O3 • US multi-city time-series studies provide strong evidence of association between short-term O3 exposure and mortality • Effects robust to confounding by copollutants Sensitive Groups for Ozone • • • • People with lung disease Children Older adults People who are active outdoors Air Pollution Disasters Donora, PA at noon on Oct. 29, 1948 London buses are escorted by lantern at 10:30 in the morning Particle pollution is a complex mixture derived from many sources Particle Deposition • Larger particles (> PM10) deposit in the upper respiratory tract • Inhalable particles (< PM10) penetrate into lungs • Some particles (e.g., less than 0.1 um) may enter bloodstream • Particles may react, accumulate, be cleared or absorbed Association Between Long Term Exposure to PM and Mortality Harvard Six-Cities Adult Cohort • • • Purpose was to study the association between pulmonary changes and long term exposure to sulfates and sulfur dioxide Enrollment 1974 – 1977 8,111 white men and women About 1,300 in each of six cities Age range 25 to 74 years Followed until 1991 (now 1999) 14 to 17 years of follow-up 111,076 person-years 1,430 death i i i i i i Dockery et al., 1993 Particle Pollution Affects the Lungs You are exposed to particle pollution simply by breathing polluted air. Exposure increases when you exercise, because you breathe more vigorously and deeply than usual. Respiratory effects include: • airway irritation • cough • phlegm • decreased lung function • airway inflammation • asthma attacks • bronchitis • chronic bronchitis And Particle Pollution Affects the Heart Particle pollution has been linked to changes that indicate your heart isn’t as healthy as it should be. Those include: • Arrhythmias and changes in heart rate. • Changes in the variability of your heart rate. • Blood component changes •C-reactive protein •Fibrinogen •Plasma viscosity •Some studies indicate that particle exposure may cause heart attacks. And particles are linked with death from heart disease. Particle exposure has been linked to heart attacks. It’s a Public Health Concern • When particles aggravate heart and lung diseases that means increases in: Hospital admissions Doctor and emergency room visits Medication use Absences from work or school • Particulate matter is linked to significant public health risks – including premature death from heart and lung disease. Living Within 300 Meters of Local Roadways Affects FEV1 Brunekreef et al., 1997 CHS: Low FEV1 at Age 18 vs. Pollution Gauderman et al., 2004 Particles Trigger Heart Attacks 1.6 1.6 1.4 1.4 Odds Ratios Odds Ratios 772 MI patients who survived 24 hours and completed interview 1.2 1.0 0.8 1.2 1.0 0 1 2 3 4 0.8 5 Hours before onset of MI Peters et al., 2001 0 1 2 3 4 Days before onset of MI 5 150 * 100 * 50 * 0 2.9 47.2 107.8 206.7 Average CAPS Concentration (m/m3) 4 Air Ratio CAPS / Pre PMNs (x10,000) PM May Cause Effects in Healthy People 3 CAPS 2 * 1 * 0 SDNN PNN50 LF Ghio et al., 2003 HF Total Devlin et al., 2003 Ratio Mechanisms of PM effects on the cardiovascular system Ambient PM Pulmonary Reflexes Pulmonary Inflammation Autonomic Nervous System Systemic Inflammation Endothelial Cell Dysfunction Conduction/Repolarization Heart Rate Cardiac Rhythm Cardiac Disruption Platelet Activation Clotting Factors Plaque Rupture Sudden Cardiac Death Thrombosis Viscosity Can We Link PM Effects with Specific Sources of Pollution? Speciation monitoring of airsheds of differing composition may enable identification of components, and sources of those components, that contribute to adverse health outcomes 100% 80% 60% 40% 20% 0% % Increase in Daily Deaths Residual Mn Salt Metals Fuel Oil Coal Mobile Crustal 15 10 * 5 * 0 -5 Crustal Coal Traffic Fuel Oil Laden et al., 2000 Monthly Asthma Admissions The Utah Valley 150 Steel Mill Closed PM (mg/m3) 125 100 75 50 25 0 1985 1986 1987 1988 80 Steel Mill Closed 60 40 20 0 1985 1986 1987 1988 Sensitive Groups for PM • • • • People with heart disease People with lung disease Older adults Children Air Quality Index Descriptors Cautionary Statement Good No message 0 – 50 Moderate 51 – 100 Unhealthy for Sensitive Groups 101 - 150 Unhealthy 151 - 200 Very Unhealthy 201 - 300 Unusually sensitive individuals Identifiable groups at risk - different groups for different pollutants General public at risk; sensitive groups at greater risk General public at greater risk; sensitive groups at greatest risk Number of Days 0 5 10 15 20 25 30 35 40 45 50 55 60 65 70 75 24-Hr PM2.5 Concentrations (µg/m3) t Typical concentrationresponse relationship A. Birmingham, AL Estimated Mortality PM Risk Assessment Typical PM2.5 distribution 5 10 15 20 25 30 35 40 45 50 55 60 65 B. 0Cincinnati, OH 24-Hr PM-2.5 Concentrations (µg/m3) 70 1.10 1.15 Typical risk distribution 1.10 1.05 1.05 1.00 1.00 20 40 60 80 100 120 140 PM 10 Mortality risk; Schwartz, 1993 20 Majority of risk from days with low-to mid-range concentrations, 40 60 80 100 120 140 not peak concentrations Total Suspended Particulates 75 Use AQI to Reduce Risk Dose = Concentration x Ventilation Rate x Time • Reduce these factors to reduce dose • Pay attention to symptoms • People with asthma – follow asthma action plan • Coaches – rotate players frequently • People with heart disease – check with your doctor AIRNow - www.airnow.gov Web Page for Health Care Providers www.airnow.gov/health-prof Ozone Web Course for Health Care Providers Medical Poster Asthma Factsheet Particle Pollution and Your Health Review Process for NAAQS Ozone NAAQS Scientific studies on health and environmental effects Scientific peer review of published studies EPA Criteria Document Reviews by CASAC and the public EPA Staff Paper Reviews by CASAC and the public PM NAAQS Final decision Public hearings and comments on proposals Proposed decision Timeline for NAAQS Reviews • Under a consent agreement for the PM and Ozone Reviews – PM Milestones • Proposed decision - December 20, 2005 • Final decision - September 27, 2006 – Ozone Milestones • February 2006 – final Criteria Document • October 2006 - final Staff Paper • March 2007 – proposed decision for public comment • December 2007 – final decision – Technology Transfer Network (TTN) for NAAQS review documents: http://www.epa.gov/ttn/naaqs/