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Human Health Effects of Particulate Matter (PM) Nathan Pechacek, M.S. Toxicology Section Texas Commission on Environmental Quality 512-239-1336

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Presentation on theme: "Human Health Effects of Particulate Matter (PM) Nathan Pechacek, M.S. Toxicology Section Texas Commission on Environmental Quality 512-239-1336"— Presentation transcript:

1 Human Health Effects of Particulate Matter (PM) Nathan Pechacek, M.S. Toxicology Section Texas Commission on Environmental Quality 512-239-1336 npechace@tceq.state.tx.us

2 PM 10 ~100 ug/m 3 PM 2.5 ~20 ug/m 3

3 PM 10 ~400-1000 ug/m 3, PM 2.5 ~60-140 ug/m 3

4 Presentation Outline Background information Health effects Challenges of epidemiological studies Sensitive populations Research needs Summary

5 Background Information on PM and the Respiratory System

6 Particulate Matter Complex substance: – Sources – Composition – Size – Travel distance – Time spent airborne

7 -reference: Brook, et al. 2004

8 Human Respiratory System -reference: USEPA, 2004

9 PM Deposition in the Respiratory System -reference: USEPA, 2003

10 PM Deposition in the Respiratory System One of the major determinants for responses Deposited PM can accumulate, translocate, and be removed Acute effects best represented by deposited dose Chronic effects best represented by retained dose Mechanisms: – Interception – Impaction – Electrostatic interaction – Sedimentation – Diffusion Site of deposition affects: – Severity of local damage – Potential for systemic effects – Clearance mechanisms

11 PM Clearance Mechanisms Often classified as absorptive or nonabsorptive Mechanisms: – Sneezing – Nose wiping and blowing – Coughing – Mucociliary transport – Dissolution and absorption in blood/lymph – Uptake by cells Time for clearance ranges from minutes to years -reference: modified from Schlesinger, 1995

12 Health Effects of PM

13 Historical PM Events of Health Significance Meuse Valley, Belgium – 1930 – PM from coal combustion – 63 dead, 6000 ill Donora, Pennsylvania – 1948 – PM from zinc smelter – 20 dead, 7000 hospitalized out of a town of 14,000 London, UK – 1952 – PM from combustion, air inversion – 3500-4000 deaths estimated originally, revised to 12,000 potential deaths

14 Types of PM Health Studies Types of studies – Epidemiological – Controlled human exposures – Animal – Molecular/Cellular/Tissue Consistency and coherence of data

15 PM Components/Parameters of Potential Interest For Health Size Surface area Number Acidity Metals Elemental and organic carbon Mass Size distribution Ions Bioaerosols Other specific toxic constituents

16 General Comments on PM Health Effects Effects may be from the inherent toxicity of the individual components of PM and/or toxicity due to general PM characteristics Emphasis on PM that reaches the lungs (  PM 10 ) – Recent focus on health effects of PM 2.5 – Health effects can result from PM  PM 10 (e.g. TSP) Effects are generally believed to be less severe unless high inherent particle toxicity or “overloading” occurs Temporary irritation to the eyes, nose, and throat is a common potential effect Both acute and chronic PM exposures are a concern Health effects associated with PM are nonspecific

17 Respiratory Effects of PM Acute symptoms: irritation, coughing, wheezing, difficulty taking deep breaths Inflammation Decreased lung function (FEV 1, FVC) Aggravate existing respiratory diseases (e.g. asthma, bronchitis, other COPD) Increases airway reactivity (response to stimuli) Increases susceptibility to respiratory infections Chronic exposure to some types of PM may result in an increased risk of respiratory cancers such as lung cancer – ex. Diesel exhaust PM

18 PM & Cardiac Effects: Challenging Toxicologists To Think Differently My toxicologists are better trained than this cat!!! Otto

19 Cardiac Effects of PM Change in blood chemistry – Can increase blood viscosity which may lead to clotting Inflammation disrupts cell function and activates platelets, which can rupture blood vessel plaques – Leads to clotting Cardiac arrhythmias – abnormal heart beats Change in heart rate variability (HRV) – Decrease in HRV is an early warning sign of potential heart attacks Aggravate existing cardiac diseases – Can potentially stimulate heart attacks in sensitive individuals

20 Cardiac Effects of PM: Change in Blood Chemistry -reference: Nadziejko, et al., 2002 Damage Repair

21 Modes of Action for Cardiac Effects Underlying mechanism(s) not known Three proposed modes of action: – Ultrafine PM ( # PM 0.1 ) enters the blood and directly exerts effects on the heart – Pro-inflammatory chemicals triggered in the alveolar region that travel in the blood and exert toxicity in the heart Cardiac effects secondary to respiratory system effects – PM can alter autonomic nervous system control of the heart Raises the possibility that heart effects are independent of adverse respiratory effects All three modes are biologically plausible – Multiple modes may be working or one mode may predominate depending on the PM characterization

22 Challenges Evaluating Epidemiological Studies

23 Association between PM and Heart Attacks -reference: Peters, 2001

24 Association between PM and Hospital Visits/Admissions -reference: USEPA, 2004

25 Association between PM and Respiratory Effects -reference: USEPA, 2002

26 Association between PM and Cardiovascular Effects -reference: USEPA., 2003

27 Issues Concerning PM & Epidemiological Studies Challenge of quantifying exposure-response relationship Consistent finding: Relatively weak positive association that is not always statistically significant – A large number of diverse studies conducted (geographical and temporal variety) Underlying biological mechanism to support epidemiological findings not known – Progress made on potential modes of action Ambient monitoring may not be an accurate assessment of personal exposure Confounding sources - other air pollutants responsible?

28 Who is Sensitive to PM It is estimated that approximately 1/3 of U.S. population is potentially sensitive to PM-related health effects However, at ambient PM levels the majority of the population is not likely to experience health effects or experiences temporary, mild effects Risk from PM is a continuum: – high early in life – low during late childhood and early adulthood – rises as one ages and risk of cardiac and/or respiratory disease increases

29 Who is Sensitive to PM? People with pre-existing cardiac and/or respiratory diseases – Severe cardiac effects can be triggered, some effects may be fatal – Respiratory diseases can be exacerbated The elderly – Greater prevalence of cardiac and respiratory diseases – PM deposition and clearance typically with age – Time to recover from effects may be extended Young children – Developing systems may be more vulnerable – PM exposure is often higher (e.g. more active outdoors) Others – people active outdoors during elevated PM – Pregnant woman?

30 Research Needs Determine the best PM parameter(s) for health effects Improve understanding of the mode/mechanism of action Concentration-response estimates Emerging effects: developmental effects Role of co-pollutants in eliciting adverse effects Further understanding of sensitive populations Placing risk from ambient PM exposure in context with other PM exposures (e.g. indoor, personal)

31 Summary PM is complex Historical events highlight that PM generates health effects, some that may be severe Importance of PM size when discussing deposition and health effects Respiratory and cardiac effects emphasized Sensitive populations for health effects Research needs


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