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    The Health Effects of AirPollution

    Robert M. OKeefe, Vice President

    Health Effects Institute

    National Workshop on Improvement of

    Urban Air Quality of Pakistan

    Lahore

    December 2004

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    Assessing the Health Effects of Air

    Pollution

    Health Effects Institute

    Air Pollution and Health Effects

    Public Health And Air Pollution in Asia

    Program PAPA The existing Asia science literature

    New Asian studies

    Conclusions

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    The Health Effects Institute

    Founded in 1980 to provide impartial, high-quality scienceon health effects of vehicle and other emissions

    Joint and Equal Core Funding from

    Government (U.S. EPA)

    Industry (28 Worldwide Vehicle Manufacturers) Today many partners worldwide: ADB, WHO, EU

    California ARB (CARB), Oil, other Industries

    Independent Expert Science Committees oversee and

    peer review all research Over 225 studies - Americas, Asia, Europe - ozone,

    carbon monoxide, particulate matter, diesel exhaust,

    benzene, butadiene, methanol, others

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    Air Pollution and Health:

    What we know about the effects

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    Air Pollution has Many Effects

    Health Respiratory, cardiovascular morbidity

    Mortality

    Heritage

    Nitric Sulfuric Acid erosion Natural Resources

    Acidification (lake and stream biology)

    Mercury deposition (fish tissue)

    Visibility

    Agriculture Ozone crop effects (~40% reduction in rice, soy yield in Pakistancity)

    *(Wahid 2003 Veranasi)

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    Many Sources of Air Pollution in

    Asia

    Combustion Open burning

    Brick Kilns

    Vehicles

    Trash burning

    Factories

    Power generation

    Cooking in slums

    Non-Combustion Agricultural

    cultivation

    Street sweeping

    Windblown sand Unpaved roads

    Paved roads(asbestos, rubberetc)

    Construction

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    Vehicle Emissions and Exposure

    Must consider all effects of the system:

    different vehicle types -

    2 and 3 wheelers cars

    trucks and buses

    vehicle plus fuels (and fuel components)

    tailpipe emissions plusevaporativeemissions

    maintenance of system

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    Major Vehicle/Fuel Emissions

    Carbon Monoxide

    Diesel Exhaust

    Particulate Matter (PM)

    Lead

    Nitrogen Oxides (NOx)

    and Hydrocarbons (HC)

    Precursors to Ozone

    and PM

    Nitrogen Dioxide

    Air Toxics

    Aldehydes

    formaldehyde

    acetaldehyde others

    Benzene

    1,3-butadiene

    Methanol Polycyclic organic

    matter (e.g. PAHs)

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    Health Effects

    Different Pollutants have Different Effects Carbon Monoxide - circulatory system, heart

    Ozone - respiratory system, lung

    Lead - nervous system, brain PM - lung, potential effects on heart

    Diesel, Air Toxics - cancer, respiratory

    effects

    There are potential effects of the Mixture

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    Health Effects

    Some populations more sensitive than others Children

    Elderly

    people with heart and lung disease Asthma is growing

    150 million asthmatics worldwide

    Increasing in most countries (2% to 5% per year)

    Asthmatics much more sensitive to air pollution

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    Particulate Matter (PM)

    Health Effects

    High levels of PM (e.g. 500 /m3) known tocause premature death

    e.g. London 1952

    Recent studies in US, Europe, Asia, South

    America have found association of PM with

    death at much lower levels (< 50ugm3)

    no evidence of a threshold (safe level) Progress made to identify a plausible

    biological mechanism for these effects;

    results not yet definitive

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    PM - The Epidemiology Studies

    A Number of Epidemiology Studies

    Europe Studies Harvard 6 Cities Study

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    PM Health Effects - India, ThailandSource: Chhabra 2001, Pande 2001, Vichit-Vadakan, 2001

    05

    10

    15

    20

    25

    30

    35

    40

    4550

    %I

    ncreaseinEffects

    Emergency

    Visits(Pande)

    Chronic

    Effects

    (Chhabra)

    Bangkok

    Asthma

    COAD

    Cardiac

    Cough

    Phlegm

    Lung Function

    Adult Resp.

    Child Resp.

    Nurse Resp.

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    Ozone Health Effects

    Known to cause inflammation in respiratory tract

    Effects have been demonstrated for short term, longterm effects are less certain

    some people appear to develop tolerance

    Reduces ability to breathe (lung function) for somepeople

    Increases hospitalization for asthma, other lungdiseases

    New US study finds Ozone mortality effects*(Domenchi et. al 2004)

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    Ozone Health Effects

    Figure 1. Individual Response to

    Ozone Exposure (after Kulle, et al,

    Am. Rev.)

    -5

    0

    5

    10

    15

    20

    25

    30

    0.1 0.15 0.2 0.25

    Ozone Concentration (ppm)

    %R

    eduction

    inFEV1

    Some humans have been shown to have reduced lungfunction (measured as FEV1) after exposure to ozone

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    Diesel Health Effects Diesel Engines have substantial advantages:

    higher fuel efficiency

    lower CO and CO2 emissions

    However, they also emit high levels of :

    particulate matter, NOx, and chemicals attached

    to the particles (e.g. PAHs)

    Two major types of health effects : acute effects (e.g. exacerbating asthma)

    cancer effects

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    Diesel Effects on Childhood Illness(Brunekreef, et al Study in 24 Dutch schools)

    1

    1.2

    1.4

    1.6

    1.8

    2

    2.2

    Increased Symptoms comparing High Truck Traffic

    >10,000) to Low Truck Traffic

    asthma

    hayfever

    phlegm

    HD allergy

    pet allergy

    wheeze last year

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    Assessing Diesel Cancer Risk

    In general, some 30 studies of effects onworkers have provided best data

    Consistent small (20-40%) increase in

    lung cancer associated with exposure Some questions about each study

    Leading International Agencies (WHO,

    IARC, US NIEHS, US EPA) haveconcluded diesel is a probable human

    carcinogen

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    Sulfur Dioxide

    Emitted from fossil fuel combustion especially from coal burning facilities, high sulfur fuels

    Can impair breathing in asthmatic children

    and adults

    Has been associated, along with PM, with increased aggravation of heart and lung disease

    premature mortality

    Recent study in Hong Kong (Lancet 2002)

    has found: substantial reductions in SO2 emissions can result in

    measurable improvements in mortality and illness

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    1988 1989 1990 1991 1992 1993 1994 1995

    0

    20

    40

    60

    80

    NO2

    SO2

    O3

    PM10

    Microgramspercubicmetre

    Year

    AIR POLLUTANT CONCENTRATIONS 1988 - 95 IN HONG KONG

    HALF YEARLY MEAN LEVELS

    Fuel restriction on sulphur

    50% reduction in SO2

    after the intervention

    No change in

    other pollutants

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    -6

    -5

    -4

    -3

    -2

    -1

    0

    15-64 65+ 15-64 65+ 15-64 65+

    REDUCTIONS IN DEATHS AFTER SULPHUR RESTRICTION

    All causes Cardiovascular Respiratory

    %R

    eductionin

    annualtrend

    -1.8%

    -2.8%

    -1.6%

    -2.4%

    -4.8%

    -4.2%

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    Air Toxics Health Effects

    Benzene

    a known human

    carcinogen

    studies in U.S. andChinese workers have

    shown link between

    exposure and

    increased leukemia

    Metals

    Range of effects,

    heart, reproductive,

    cancers

    1,3 Butadiene

    a probable or

    known human

    carcinogen studies in laboratory

    animals and US and

    Czech workers have

    shown effects

    Aldehydes, PAHs

    Cancers, Irritants

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    Air Pollution and Health in Asia:The Public health and Air Pollution Program

    (PAPA)

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    The Problem: Air Pollution in Asia:High Levels in Many Cities (2000-2001)

    Source: Benchmarking Report on Air Quality in Asian cities Stage 2, 2004 (forthcoming)

    SPM Limit = 90 g/m3 (WHO, 1979)

    0

    50

    100

    150

    200

    250

    300

    350

    400

    concentrationin

    g/m

    3

    SO2 NO2 SPM PM10

    PM10Limit = 50 g/m3 (USEPA, 1997)

    SO2Limit = 50 g/m3 (WHO, 1999)

    NO2Limit = 40 g/m3 (WHO, 1999)

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    Lancet

    October,

    2002

    E i l B d

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    Environmental Burdens

    Premature Deathssource: WHO Global Burdon of Disease

    EEnnvviirroonnmmeennttaallRRiisskkss

    GGlloobbaallEEssttiimmaattee

    AAssiiaannEEssttiimmaattee((SSEEAARR++WWPPRR))

    AAssiiaaaassaappeerrcceennttooffGGlloobbaall

    UUnnssaaffeeWWaatteerr 11,,773300,,000000 773300,,000000 4422%%

    UUrrbbaannOOuuttddoooorrAAiirr

    779999,,000000 448877,,000000 6611%%

    IInnddoooorrAAiirr 11,,661199,,000000 11,,002255,,000000 6633%%

    LLeeaadd 223344,,000000 8888,,000000 3377%%

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    The Challenge: Expanding current science

    base to inform Asian air regulatory decisions

    Air pollution poses clear health effects

    Western research is relevant to Asian populations,

    however extrapolation poses challenges

    Population characteristics Pollution sources and mixes

    Are observed risks similar?, greater?, smaller?

    A clear need for representative air pollution & healthstudies of local Asian populations

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    PAPA Program Partnership with CAI-ASIA to understand the health effects of air

    pollution in Asia, now and in the future

    Active effort underway:

    Published Scienti f ic Reviewand Meta Analysisof what is knowntoday about health effects in Asian cities

    Conducting ser ies of epidemio logical stud iesin representative

    Asian cities Understand local impact

    Combine to provide Asia-wide understanding

    Publish a Comprehensive Assessmentof the state of air pollutionand health across Asian cities

    Bui ld capaci tyof local scientists

    Overal l Goal: Quality science to inform key Asian regulatory & policy

    decisions

    Health Effects of Outdoor Air Pollution

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    Health Effects of Outdoor Air Pollution

    in Developing Countries of Asia: A

    Literature Review Systematic identification of 140

    peer-reviewed Asian studies1980-2003

    Special focus on studies of daily

    changes in air pollution andhealth

    Conduct first ever Asian metaanalysis quantifying risks,finding initial similarities with

    West

    Identify knowledge gaps toguide future research

    Active communication to policy

    makers

    St di f Ai P ll ti d H lth i A i 1980 2003

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    Studies of Air Pollution and Health in Asia 19802003

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    Many Health Effects Studied

    0

    2

    4

    6

    8

    10

    12

    All-Cause

    Mortality

    Respiratory

    Mortality

    Cardiovascular

    Mortality

    Respiratory

    Hospital

    Admissions

    Cardiovascular

    Hospital

    Admissions

    Outcome Diagnosis

    NumberofStud

    ies

    TSP

    PM10

    PM2.5

    SO2

    NO2

    CO

    O3

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    Daily Mortality: Initial Results:

    Asian Risk Estimates Similar to West

    0.460.62 0.49

    0

    0.10.2

    0.3

    0.4

    0.5

    0.6

    0.7

    Percent

    Increase

    US(90 Cities)* Eur(21 Cities)* Asia (4 Cities)

    Percent Increase in Mortality per 10 micrograms of

    Exposure

    * Estimates Using Pre-GAM Results (without revision)

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    PAPA:Looking Ahead

    A Special Challenge: Understanding the interactionamong air pol lut ion , poverty, and heal th In Asia high levels of air pollution, dense population,

    extensive poverty are prevalent

    Some initial evidence (mostly from West) that the poor

    face worse effects from air pollution Could be due to:

    Different exposures (roadside, indoor, occupational)

    Poorer SES\health status (nutrition, medical care) leading tohigher susceptibility

    Other factors Potential Public health implications could be significant

    New study under design in Ho Chi Minh City tounderstand poverty effects

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    Conclusions Air Pollution from many sources, including vehicles,

    fuels have been shown to have effects on mortality,morbidity

    Problem will grow with economic expansion

    WHO estimates place air pollution mortality in hundreds

    of thousands across South Asia, Eastern Mediterraneanregion (including Pakistan)

    While studies are extrapolated from developed world,initial PAPA Review and analysis tend to confirm resultsin Asian populations, though many limitations exist

    The PAPA program is building a better base of Asianhealth and air pollution science New studies across Asia, with capacity building as a priority

    Role of poverty in air pollution to be assessed

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    Conclusions

    Better air monitoring needed over long term To determine current status, monitor ongoing

    progress and assess health, communicate to

    public However, Pakistan urban conditions alsowarrant near term action Visible emissions wide-spread

    Dense population level, clear exposure

    Acute effects commonplace

    Provided basis of action in many countries (UK,HK, others) beforecomprehensive monitoring

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    Thank You!

    Bob OKeeferokeefe @healtheffects.org

    www.healtheffects.org