Human Health Effects of Particulate Matter PM Nathan

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Human Health Effects of Particulate Matter (PM) Nathan Pechacek, M. S. Toxicology Section Texas

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

PM 10 ~100 ug/m 3 PM 2. 5 ~20 ug/m 3

PM 10 ~100 ug/m 3 PM 2. 5 ~20 ug/m 3

PM 10 ~400 -1000 ug/m 3, PM 2. 5 ~60 -140 ug/m 3

PM 10 ~400 -1000 ug/m 3, PM 2. 5 ~60 -140 ug/m 3

Presentation Outline l Background information l Health effects l Challenges of epidemiological studies l

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

Background Information on PM and the Respiratory System

Background Information on PM and the Respiratory System

Particulate Matter l Complex substance: – Sources – Composition – Size – Travel distance

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

-reference: Brook, et al. 2004

-reference: Brook, et al. 2004

Human Respiratory System -reference: USEPA, 2004

Human Respiratory System -reference: USEPA, 2004

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

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

PM Deposition in the Respiratory System One of the major l Mechanisms: determinants for

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

PM Clearance Mechanisms Often classified as absorptive or nonabsorptive l Mechanisms: l Sneezing Nose

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

Health Effects of PM

Health Effects of PM

Historical PM Events of Health Significance l Meuse Valley, Belgium – 1930 – PM

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

Types of PM Health Studies l Types of studies – Epidemiological – Controlled human

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

PM Components/Parameters of Potential Interest For Health l l l Size Surface area Number

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

General Comments on PM Health Effects may be from the inherent toxicity of the

General Comments on PM Health Effects may be from the inherent toxicity of the individual components of PM and/or toxicity due to general PM characteristics l Emphasis on PM that reaches the lungs ( PM 10) l – Recent focus on health effects of PM 2. 5 – Health effects can result from PM PM 10 (e. g. TSP) l l 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 l Health effects associated with PM are nonspecific l

Respiratory Effects of PM l l l l Acute symptoms: irritation, coughing, wheezing, difficulty

Respiratory Effects of PM l l l l 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

PM & Cardiac Effects: Challenging Toxicologists To Think Differently Otto My toxicologists are better

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

Cardiac Effects of PM l Change in blood chemistry – Can increase blood viscosity

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

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

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

Modes of Action for Cardiac Effects Underlying mechanism(s) not known l Three proposed modes

Modes of Action for Cardiac Effects Underlying mechanism(s) not known l Three proposed modes of action: l – 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 l Cardiac effects secondary to respiratory system effects – PM can alter autonomic nervous system control of the heart l l 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

Challenges Evaluating Epidemiological Studies

Challenges Evaluating Epidemiological Studies

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

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

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

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

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

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

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

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

Issues Concerning PM & Epidemiological Studies Challenge of quantifying exposure-response relationship l Consistent finding:

Issues Concerning PM & Epidemiological Studies Challenge of quantifying exposure-response relationship l Consistent finding: Relatively weak positive association that is not always statistically significant l – A large number of diverse studies conducted (geographical and temporal variety) l 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 l Confounding sources - other air pollutants responsible? l

Who is Sensitive to PM It is estimated that approximately 1/3 of U. S.

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

Who is Sensitive to PM? l People with pre-existing cardiac and/or respiratory diseases –

Who is Sensitive to PM? l 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 l The elderly – Greater prevalence of cardiac and respiratory diseases – PM deposition and clearance typically with age – Time to recover from effects may be extended l Young children – Developing systems may be more vulnerable – PM exposure is often higher (e. g. more active outdoors) l Others – people active outdoors during elevated PM – Pregnant woman?

Research Needs l l l l Determine the best PM parameter(s) for health effects

Research Needs l l l l 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)

Summary l l l PM is complex Historical events highlight that PM generates health

Summary l l l 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