AREP GURME Section 6 Health Effects AREP GURME A Brief History of PM Section 6 – Health Effects.
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Transcript AREP GURME Section 6 Health Effects AREP GURME A Brief History of PM Section 6 – Health Effects.
AREP
GURME
Section 6
Health Effects
AREP
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A Brief History of PM
Section 6 – Health Effects
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The Houses of Parliament, Stormy Sky
Claude Monet, 1904
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Air Pollution Disasters
1930 Meuse River Valley, Belgium
A three-day episode of severe air pollution makes 6,000 ill and kills 63.
1948 Denora, PA
1952 London, England
Oct. 26 to 31: air pollution episode
leaves 20 dead out of 14,000 persons.
Dec. 4 to 9: “Killer Fog” leaves three
to four thousand people dead.
Donora, PA at noon on
Oct. 29, 1948
London buses are escorted by lantern
at 10:30 in the morning.
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Human Lung
Air conducting
•Trachea
•Bronchi
•Bronchioles
Gas exchange
•Respiratory
bronchioles
•Alveoli
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Mouse lung exposed to Diesel Exhaust
Exposed mouse lung
Normal mouse lung
Diesel Exhaust Particles (DEP) augment inflammation by increasing
receptors for bacterial lipopolysaccharide. The effect is to make the lungs
highly sensitive to the presence of normal levels of bacteria. This results in
greatly heightened production of pro-inflammatory mediators from the
cells.
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Mortality attributed to London Smog
Schwartz, 1994
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Outdoor Air Pollution
Regulatory Categories
Criteria Pollutants
• Present everywhere
• Ambient air quality standards
• Widely monitored
Air toxics
• Long list (>180)
• Many carcinogens
• Less frequent ambient measurements
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Criteria Pollutants
• Particulate matter
•
•
•
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•
– PM10 (PM < 10 microns)
– PM2.5 (PM < 2.5 microns)
– (PM10-PM2.5 = coarse fraction)
Nitrogen dioxide (NO2)
Sulfur dioxide (SO2)
Ozone (O3)
Carbon monoxide
Lead
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Disease and environmental factors
Estimates of the burden of disease attributable
to environmental factors vary depending on
–
–
–
–
–
Type of disease
Vulnerability
Genetics
Population group
Socioeconomic aspects
Large differences between people living in
– Industrialized/developing countries
– East/West of Europe
– and others
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Disease and environmental factors
Major health impacts and their association with
environmental factors
Cancer: air pollution, mainly PM 2.5 and smaller, PAHs,
metals (AS Cd Cr)
Cardiovascular disease: air pollution (CO, O3, PM, Pb)
Respiratory diseases: SO2, NO2, PM10 and PM 2.5, O3
Developmental disorders: Pb, Hg, Cd
Nervous system disorders: Pb, PCBs, Methyl Hg, Mn
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Disease and environmental factors
Air pollution is the environmental factor with the greatest
health impact in Europe!
Effect is expressed by number of deaths (mortality
rates), and by DALYs:
– “Disability-Adjusted Life Years”
– An indicator of “burden of disease”,
– Gives an indication how disease can alter the ability of people
to live a normal life compared with those with no disease.
Expresses years of lost life.
Effect also expressed as morbidity, such as increased
frequency of chronic bronchitis, respiratory hospital
admissions, restricted activity days.
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Disease and environmental factors
WHO estimates for Europe (51 countries)
• Children age 0-4 years: 1.8 – 6.4 % of deaths from all causes due
to outdoor air pollution
• Mild mental retardation due to lead exposure: 4.4 % of all DALYs
In a selection of European cities each year:
• Air pollution responsible for 100 000 deaths and
• 725 000 years of lost life (DALYs)
European Commission estimates in CAFÉ:
• 350 000 premature deaths in 2000 due to outdoor air pollution of
PM2.5 alone =
• Average loss of life expectancy of 9 months for each European
citizen
Ozone causes 20 000 premature deaths annually
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Disease and environmental factors
Heat waves cause excess deaths; however,
large portion due to air pollution
Heat wave in Europe summer 2003, in United
Kingdom:
• 2045 excess deaths 4-13 August (compared with
1998-2002 average)
• Deaths due to air pollution:
– 225 – 593 due to ozone
– 207 due to PM10
– Above represent 21 – 38 % of the excess deaths
(John R. Stedman)
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Disease and environmental factors
Strength of association between environmental factors
and selected diseases, corresponding population
impact and prevention possibilities (EEA and IPCC)
• Neurodevelopment (Pb): very likely 90-99 %, moderate, high
• Neurodevelopment (Hg): very likely 90-99 %, low, high
• Respiratory diseases (air pollution): very likely 90-99 %,
high, moderate
• Asthma causation (air pollution): medium likelihood 33-66 %,
high, moderate
Many examples show that respiratory health and life
quality improves with improved air quality.
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Strength of association between environmental factors and
selected diseases, corresponding population impact and
prevention possibilities (EEA and IPCC)
Neurodevelopment (Pb): very likely 90-99 %, moderate, high
Neurodevelopment (Hg): very likely 90-99 %, low, high
Respiratory diseases (air pollution): very likely 90-99 %, high,
moderate
Asthma causation (air pollution): medium likelihood 33-66 %,
high, moderate
Many examples show that respiratory health and life quality
improves with improved air quality.
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PM is derived from
many different sources
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Particulate Matter
Sizes and Composition
Fine
Coarse
Ultra Fine
Natural:
Soil
Dust
Seasalt
Bioaerosols
Anthropogenic:
Sulfates
Nitrates
Ammonia
Carbon
Lead
Organics
0.1 um
1 um
2.5 um
10 um
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PM relative to hair cross section
Hair cross section (60 mm)
Human Hair
PM10
(10 mm)
PM2.5
(2.5 mm)
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Particles Affect the Lungs
Respiratory system effects:
Respiratory symptoms – irritation of
airways, cough
Decreased lung function
Airway inflammation
Asthma attacks, bronchitis
Chronic bronchitis
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Public Health Risks Are Significant
Particles are linked to:
Premature death from heart and lung
diseases
Aggravation of heart and lung diseases,
with increased:
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•
Hospital admissions
Doctor and ER visits
Medication use
School and work absences
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Some Groups Are More at Risk
People with heart or
lung disease
Greater deposition
with chronic
obstructive
pulmonary disease
(COPD)
Older adults
Greater prevalence of
heart and lung
disease
Children
• More likely to be active
• Breathe more air per kg
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Nitrogen dioxide (NO2)
Emissions from high temperature combustion
processes: motor vehicle exhaust and
stationary sources for power production
Exposures indoors due to (unvented) gas
appliances and infiltration of ambient NO2
(Complex atmospheric chemistry – can be
transformed to HNO3 and nitrate particles)
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Nitrogen dioxide (NO2) effects
Strong oxidant and respiratory irritant
(forms nitrous and nitric acids in contact
with water)
NO2 irritates the nose, throat and lungs
especially in people with asthma.
Lowers resistance to respiratory infections
such as influenza.
Contributes to ozone formation (and thus
to ozone effects indirectly).
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Sulfur dioxide (SO2)
Irritant gas resulting mainly from
combustion of sulfur-containing fossil
fuels (power plants, large industrial
facilities, diesel vehicles) and metal
smelting.
(Is oxidized/hydrated to form sulfuric acid
particles)
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SO2 Effects
Usually short-term concentration peaks
SO2 reduces lung function:
Constricts breathing passages, causing
wheezing, shortness of breath and coughing,
happens quickly.
Lung function returns to normal about an hour
after exposure ends.
Causes above in healthy subjects and
asthmatics; latter are substantially more
sensitive
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Ozone (O3)
Ubiquitous exposure - formed by natural
processes as well as human activities
Principal constituent of photochemical
smog – not emitted directly
Highly reactive, but poorly soluble,
allowing deep lung penetration
Acute toxicity is related to dose =
Concentration x Ventilation Rate x Time
– increased risk from outdoor exertion
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Ozone Irritates Airways
Symptoms:
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Cough
Sore or scratchy throat
Pain with deep breath, or chest pain
Fatigue
Rapid onset, but effect is greater 24 hours
after exposure
Similar symptoms for people with or
without asthma
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Public Health Risks Are Significant
Ozone is linked to:
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Aggravation of lung diseases, increased
Hospital admissions
Doctor and ER visits
Medication use
School and work absences
Permanent lung changes
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Public Health Risks Are Significant
Respiratory Admissions
Respiratory hospital admissions by daily maximum
ozone level, lagged one day
114
112
110
108
106
104
102
.01 .02 .03 .04 .05 .06 .07 .08 .09 .1
Ozone concentration (ppm)
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(Burnett et al, 1994)
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Some Groups Are More at Risk
Children and adults who are active
outdoors
People with lung diseases, such as
asthma
People who are unusually sensitive to
ozone
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Air Quality Index
Descriptors
Cautionary Statement
Good
No message
0 – 50
Moderate 51 – 100
Unusually sensitive individuals
Unhealthy for
Sensitive Groups
101 - 150
Identifiable groups at risk - different groups
for different pollutants
Unhealthy
151 - 200
General public at risk; sensitive groups at
greater risk
Very Unhealthy
201 - 300
General public at greater risk; sensitive
groups at greatest risk
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Use AQI to Reduce Risk
Dose = Concentration x Ventilation rate x
Time
• Reduce concentration – schedule
activities when pollution levels lower
• Reduce ventilation rate by taking it easier
• Reduce time spent in vigorous outdoor
activities
Pay attention to symptoms
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Health advisories make a difference
Roper 2002 survey of 2000 people across
the US:
• 52 % had heard of AQI “Code Orange” or
“Code Red” air quality days
• Of those, 46 % have reduced exposure to
air pollution
UCLA – Neidell et al.:
• 4 to 7 % reduction in pediatric hospital
admissions for asthma attributable to
advisories
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Will It Matter if Air Pollution
Decreases?
The Dublin Experience
• Dublin’s air quality deteriorated in the 1980s after a switch
from oil to cheaper bituminous coal for heating.
• In 1990 the Irish Government banned the use of bituminous
coal within the city of Dublin, resulting in a reduction in PM
concentrations.
• Change in age-standardized total, cause-specific, and agespecific mortality rates for Dublin County Borough for 72
months before and after ban of sale of coal in Dublin:
decrease from 4.5 to 15.5 % depending on the specific
group.
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The Utah Valley
Monthly Asthma Admissions
Steel mill closed due to a labor dispute
150
Steel Mill
Closed
PM (mg/m3)
125
100
75
50
25
0
1985
1986
1987
80
60
Steel Mill
Closed
40
20
0
1988
1985 1986
1987
1988
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Example of Action
Phasing out leaded gasoline
Mental retardation due to lead exposure
was estimated to be nearly 30 times
higher in regions where leaded gasoline
was still being used compared with
regions where leaded gasoline had
been completely phased out.
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Information sources
Talks by:
• Susan Lyon Stone, Michael Lipsett
• Robert Devlin, John R Stedman
Guidelines on Biometeorology and Air Quality
Forecasts, WMO, Public Weather Service
Environment and Health, EEA Rep No 10/2005
Preventing disease through healthy
environments, WHO, 2006
EPA (US), AIRNow: www.airnow.gov
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Need Chemical Weather Forecasting
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