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The Science Behind the Particulate Matter (PM) Standards

The Science Behind the Particulate Matter (PM) Standards . George Thurston, Sc.D. New York University School of Medicine NYU-EPA PM Center, Deputy Director Tuxedo, NY 10987. State of the Science in 1998.

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The Science Behind the Particulate Matter (PM) Standards

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  1. The Science Behind theParticulate Matter (PM) Standards George Thurston, Sc.D. New York University School of Medicine NYU-EPA PM Center, Deputy Director Tuxedo, NY 10987

  2. State of the Science in 1998 •Dozens of epidemiology studies from around the world reported associations between ambient PM and cardiac mortality and morbidity • PM levels are very low compared with other particle exposures: One cigarette = 10x more than typical 24 hour exposure to PM • No widely accepted patho-physiological pathway or mechanism could explain how a person could die from exposure to PM at such low levels of air pollution. EPA Particulate Matter Research Centers Program

  3. The Epidemiological Pyramid of Air Pollution Effects

  4. People Most Affected by Ambient Air Pollution • Older Adults • Persons with Pre-Existing Respiratory Disease (e.g., Chronic Obstructive Pulmonary Disease, COPD, such as emphysema, those with Cardiac problems) • Children, especially those with Asthma. • Healthy adults who work or exercise outdoors. • Persons with inadequate health care, such as the poor and working poor.

  5. Particle Deposition in the Lung The very smallest (ultrafine) particles may enter the blood and travel throughout the body. Larger particles deposit in the upper airways (nose and throat) and are cleared out Smaller particles penetrate deep into the lungs and stay there longer

  6. A Key Question in 1998: EPA Particulate Matter Research Centers Program

  7. WHAT WE HAVE LEARNED IN RECENT YEARS EPA Particulate Matter Research Centers Program

  8. EPA Particulate Matter Research Centers Program

  9. EPA Particulate Matter Research Centers Program

  10. EPA Particulate Matter Research Centers Program

  11. EPA Particulate Matter Research Centers Program

  12. EPA Particulate Matter Research Centers Program

  13. EPA Particulate Matter Research Centers Program

  14. EPA Particulate Matter Research Centers Program

  15. EPA Particulate Matter Research Centers Program

  16. Elevated CRP, a known cardiac risk factor, is associated with oxidative stress EPA Particulate Matter Research Centers Program

  17. Other Epidemiology Also Confirms a Rise in C-Reactive Protein (CRP) during Higher PM (Source: Peters et al, EHJ, 2001) EPA Particulate Matter Research Centers Program

  18. Acidic Sulfates, Transition Metals, and Oxidative Stress • Transition metals (e.g., Fe and V) can mediate electron transfer via Fenton Reactions causing oxidative stress. • Oxidative Stress (OS) can lead to cellular damage: • OS is known to be involved in inflammation, tissue aging, cardiac ischemia, arthritis, cancer, and fibrosis (Mossman and Marsh, 1989, Janssen et al, 1993, Costa et al, 1989a, 1989b; Ewing, 1983; Slaga, 1983; Harman, 1981). • The presence of acids in a particle greatly enhance the transition metals’ solubility and, therefore, their bio-availability, increasing OS. • E.g., See Veronesi et al., 1999, Toxicol. Appl. Pharmacol., 155:106-115; Carter et al., 1997, Toxicol. Appl. Pharmacol., 146:180-188; and Chen et al. 1990, J. Toxicol. Environ. Hlth. 29:169-184.

  19. EPA Particulate Matter Research Centers Program

  20. Chen et al., JAMA (in press), 2005 EPA Particulate Matter Research Centers Program

  21. EPA Particulate Matter Research Centers Program

  22. Toxicology Progress Summary

  23. Epidemiologic Evidence AlsoStrengthened Since 1998 • More than 100 new short-term studies confirming the fine particle-mortality and morbidity associations. • An extended analysis of the original American Cancer Society (ACS) prospective cohort study confirmed previous results, and found associations between long-term exposure and lung cancer.

  24. Mortality Risks of Long-Term Fine PM Increase with Increasing Exposure (Pope, Burnett, Thun, Calle, Krewski, Ito , and Thurston) (JAMA, 2002)

  25. JAMA Study Conclusions • Long-term exposure to fossil fuel combustion air pollution, and especially to fine particulate matter, is associated with increased annual risk of mortality. • For lung cancer, living in a more polluted city is associated with approximately a 20% increase in residents’ risks of dying from lung cancer. • This is roughly comparable to the cancer risk of passive smoking exposure from living with a smoker. • The cancer risk from air pollution appears greatest for non-smokers and those with lower socio-economic status.

  26. Cardiovascular Mortality Most Affected by Long Term Particulate Matter Air Pollution Exposures Relative Risks and 95%ile CI’s for a 10 ug/m3 increase in Annual PM2.5 mass concentration (SOURCE: Pope, Burnett, Thurston, Thun, Calle, Krewski, and Godleski, CIRCULATION, 2004)

  27. Diesel Particles Have Been Identified to Among Those Especially Toxic • Diesel Particles are in the fine fraction that gets into the deepest parts of the lung. • Diesel exhaust contain irritants and cancer-causing substances (e.g., BaP, benzene). • European studies show higher rates of asthma problems near heavy vehicle traffic. • Experimental studies show that exposure to diesel particles increases asthma reactions (e.g., IgE immuno-globulin antibody production).

  28. Diesel Particles Induce Asthma Allergic Reactions(Diaz-Sanchez, et al., J.Clin. Invest. 1994) DEP Challenged Saline Challenged 1.6 1.2 IGE (ng/ml) 0.8 0.4 0 Day 0 Day 4 Day 7 Day 10 The effect of DEP on immunoglobulin levels and albumin in nasal washes over time. Subjects were challenged intranasally with either 0.3mg of DEP 200 ml of saline or 200 ml of saline alone.

  29. NYU STUDY TO INVESTIGATE TRAFFIC RELATED AIR POLLUTION: EXPOSURES AND EFFECTS AMONG CHILDREN WITH ASTHMA IN THE SOUTH BRONX, NY Nelson Institute of Environmental Medicine Department of Environmental Medicine NYU School of Medicine Tuxedo, NY

  30. Study Design • Group of ten elementary-school children with asthma from each of four South Bronx elementary schools were followed for a month at each school. • The subjects’ personal respiratory symptoms, lung function, activity pattern data, and personal air pollution exposures were collected at the same time.

  31. Students Used Wheeled Backpack for Personal Air Sampling

  32. Study Conducted at 4 Bronx Schools • PS 154 (Spring, 2002) • 33 East 135 Street • Next to the Major Deegan Highway • MS 302 (Spring, 2004) • 681 Kelly Street • Four Blocks West of the Bruckner Expressway • CS 152 (Fall, 2004) • 1007 Evergreen Avenue • Next to the Bruckner Expressway • MS 201 (Spring, 2005) • 730 Bryant Avenue • Hunts Point, 6 Blocks East of the Bruckner

  33. Traffic Impact Highest at Schools Beside the Bronx’s Highways (30-50% higher)

  34. Lung Function “Peak Flow” was More Negatively Associated with Traffic Particles than PM2.5 in General

  35. Asthma Symptoms Nearly Double on High Traffic Pollution (EC) Days

  36. Study Conclusions To Date • Traffic pollution is a significant contributor to asthma problems among children in the South Bronx. • Peak outdoor soot (EC) concentrations at the NYU van were correlated with peak truck traffic periods. • Daily Symptoms and lung function analyses results indicate that traffic soot (EC) particles are more related to lung function and asthma symptoms than PM2.5 in general. • Health effects associations with Elemental Carbon remain significant, even when Ozone and Ambient Temperature are considered.

  37. Overall Implications • New toxicological research has shown numerous effects and pathways of PM effects indicating that the epidemiological associations with morbidity and mortality are biologically plausible at ambient levels of PM2.5. • New epidemiological research has shown significant mortality and morbidity effects below the present PM2.5 standards, supporting the setting of new U.S. standards at the lower end of the EPA Staff Paper’s range of PM2.5 standard options.

  38. Acknowledgements The Toxicology Progress portion of this presentation was based largely on progress reports presented at the most recent PM Center Directors’ meeting in Washington, DC in October, 2004, including: • Dr. Morton Lippmann, NYU • Dr. Lung Chi Chen, NYU • Dr. Robert Devlin, U.S. EPA

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