Air Pollution Reduction:
Is it Real and Does it Work?
C. Arden Pope III
Mary Lou Fulton Professor of Economics
Presented at:
Frontiers in Spatial Epidemiology
Imperial College of London, Natural History Museum of London
November 5-6, 2012
Illustration for Charles Dickens’
Sketches by Boz, by George Cruikshank, 1838
The chimney, smoke Stack, and smoke and fog (smog) have long played important iconic roles in the art and literature of London.
Over London by Rail, 1870 Gustave Doré
Depicts the congested and polluted Industrial environment of 1870 London
Coffee Stall by
Gustave Doré,
In a description of arepresentative London Fog day (April 6, 1870) Doré’s friend Blanchard Jerrold say’s of an experience with Doré:
“We were well into the morning— and it was as dark as the darkest midnight. . . It was choking: it made the eyes ache.”
From:
London: A pilgrimage, 1872 and
Doré’s London: All 180 illustrations from London, A Pilgrimage, 2004
Claude Monet, Houses of Parliament, London, 1903
Claude Monet, Houses of Parliament, London, 1904
Claude Monet, Waterloo Bridge, London, 1903— Zoom in on background of pollution
Classical Economics
• Adam Smith— Wealth of Nations (1776),
free markets, competition, and the
metaphor of the “
invisible hand
”.
• “
Laissez-faire
”
• What about air pollution?
Smells like
Meuse Valley, Belgium Smog, December 1-5, 1930 --60 deaths, 10 time expected
Donora, PA
(Severe episode, Oct. 27-31, 1948)
From, Public Health Service, Bulletin No. 306, 1949
Danora, PA. Noon, Oct 29, 1948.
http://www.weather.com/multimedia/videoplayer.html?clip=12603&collection=257&fro m=sitemap
Donora, PA—administering oxygen --Approx. 20 deaths, 6 times expected
London Fog Episode, Dec. 1952
Loss of Faith in the doctrine of Laissez-faire
• No longer did air pollution “smell like money” but it
smelled like something unhealthy.
• In the UK, US, and elsewhere there were public policy
efforts to clean up the air and eliminate the “Killer Smog
Episodes.” (Clean air act)
• There was success at eliminating or reducing the
extreme air pollution episodes but air pollution remained
and we learned that even moderate air pollution had
Brief methodological outline of air
pollution epidemiological studies:
Studies of short-term exposure
Episode
Population-based daily time-series
Panel-based acute exposure
Case-crossover
Studies of long-term exposure
Population-based cross-sectional
Cohort-based mortality
Cohort- and panel-based morbidity
Case-control studies
Intervention/natural experiment
Exploit temporal variability Exploit spatial variability Exploit both temporal and spatial variabilityBrief methodological outline of air
pollution epidemiological studies:
Studies of short-term exposure
Episode
Population-based daily time-series
Panel-based acute exposure
Case-crossover
Studies of long-term exposure
Population-based cross-sectional
Cohort-based mortality
Cohort- and panel-based morbidity
Case-control studies
Intervention/natural experiment
Exploit temporal variability Exploit spatial variability Exploit both temporal and spatial variabilityMedian PM2.5 for aprox. 1980 8 10 12 14 16 18 20 22 24 26 28 30 32 34 A d ju s te d Mor ta lit y f o r 1 9 8 0 (De a th s /Y r/ 1 0 0 ,0 0 0 ) 600 650 700 750 800 850 900 950 1000
Mean sulfate for aprox. 1980
4 6 8 10 12 14 16 18 20 22 24 A d ju s te d Mor ta lit y fo r 1 9 8 0 (De a th s /Y r/ 1 0 0 ,0 0 0 ) 600 650 700 750 800 850 900 950 1000
Mean PM2.5 for aprox. 1980
8 10 12 14 16 18 20 22 24 26 28 30 32 34 600 650 700 750 800 850 900 950 1000
Mean TSP for aprox. 1980
15 30 45 60 75 90 105 120 135 150 165 600 650 700 750 800 850 900 950 1000
Figure 1. Age-, sex-, and race-adjusted population-based mortality rates in U.S. cities for 1980 plotted over various indices of particulate air pollution.
Age-, sex-, and race- adjusted population-based mortality rates in U.S. cities for 1980 plotted over various indices of particulate air pollution (From Pope 2000).
Brief methodological outline of air
pollution epidemiological studies:
Studies of short-term exposure
Episode
Population-based daily time-series
Panel-based acute exposure
Case-crossover
Studies of long-term exposure
Population-based cross-sectional
Cohort-based mortality
Cohort- and panel-based morbidity
Case-control studies
Intervention/natural experiment
Exploit temporal variability Exploit spatial variability Exploit both temporal and spatial variabilityAn Association Between Air Pollution and
Mortality in Six U.S. Cities
1993
Dockery DW, Pope CA III, Xu X, Spengler JD, Ware JH, Fay ME, Ferris BG Jr, Speizer FE.
Methods:
14-16 yr prospective follow-up of 8,111 adults living in
six U.S. cities.
Monitoring of TSP PM
10, PM
2.5, SO
4, H
+, SO
2
, NO
2, O
3.
Data analyzed using survival analysis, including
Cox Proportional Hazards Models.
Controlled for individual differences in: age, sex, smoking,
Average Polluted cities Highly Polluted cities Clean cities
Cox Proportional Hazards Survival Model
Cohort studies of outdoor air pollution have commonly used the CPH Model to relate survival experience to exposure while simultaneously controlling for other well known mortality risk factors. The model has the form
(
)
)
(
)
(
0
(
)
(
)
)
(
t
x
exp
t
t
l
T
i
l
l
i
Hazard function or instantaneous probability of death for the ithsubject in the lth strata. Baseline hazard function, common to all subjects within a strata.
Regression equation that modulates the baseline hazard. The vector Xi(l)
contains the risk factor information related to the hazard function by the regression vector β which can vary in time.
Adjusted risk ratios (and 95% CIs) for
cigarette smoking and PM
2.5
Cause of
Death
Current Smoker,
25 Pack years
Most vs. Least
Polluted City
All
2.00
(1.51-2.65)1.26
(1.08-1.47)Lung
Cancer
8.00
(2.97-21.6)1.37
(0.81-2.31)Cardio-pulmonary
2.30
(1.56-3.41)1.37
(1.11-1.68)All
other
1.46
(0.89-2.39)1.01
(0.79-1.30)Particulate Air Pollution as a Predictor of Mortality in a
Prospective Study of U.S. Adults
Pope CA III, Thun MJ, Namboodiri MM, Dockery DW, Evans JS, Speizer FE, Heath CW Jr.
1995
Methods:
Linked and
analyzed ambient air
pollution data from
51-151 U.S. metro areas
with risk factor data for
over 500,000 adults
enrolled in the
ACS-CPSII cohort.
Clark Heath Michael Thun
Adjusted mortality risk ratios (and 95% CIs) for cigarette
smoking the range of sulfates and fine particles
Cause of
Death
Current
Smoker
Sulfates
Fine
Particles
All
2.07
(1.75-2.43)1.15
(1.09-1.22)1.17
(1.09-1.26)Lung
Cancer
9.73
(5.96-15.9)1.36
(1.11-1.66)1.03
(0.80-1.33)Cardio-
Pulmonary
2.28
(1.79-2.91)1.26
(1.16-1.37)1.31
(1.17-1.46)All other
1.54
(1.19-1.99)1.01
(0.92-1.11)1.07
(0.92-1.24)Legal uncertainty largely
resolved with 2001
unanimous ruling by the
U.S. Supreme Court.
Dan Krewski Rick Burnett Mark Goldberg and 28 others
Cox Proportional Hazards Survival Model
Cohort studies of outdoor air pollution have commonly used the CPH Model to relate survival experience to exposure while simultaneously controlling for other well known mortality risk factors. The model has the form
(
)
)
(
)
(
0
(
)
(
)
)
(
t
x
exp
t
t
l
T
i
l
l
i
Hazard function or instantaneous probability of death for the ithsubject in the lth strata. Baseline hazard function, common to all subjects within a strata.
Regression equation that modulates the baseline hazard. The vector Xi(l)
contains the risk factor information related to the hazard function by the regression vector β which can vary in time.
Note: We have extended this basic model to deal with random effects (spatial
Further extension of the Cox Proportional Hazards model to allow for random effects (spatial clustering) and to include spatial socioeconomic and
environmental (contextual) variables at two spatial levels (zip code and MSA). Contextual variables included: Poverty (%), Income disparity (Gini), Median
Household income, Unemployment (%), Not white (%), Grade 12 education (%), Air conditioning (%).
Sources Data/ periods Model Strata Individual risk factor variables Ecological/contextual spatial variables Spatial smoothing? % increase/10 µg/m3 All- Cardio- Cause pulmonary Lave/Seskin 1977, Ozkaynak/ Thurston 1987 U.S. pop.-based mortality rates OLS or WLS cross-sectional regression models
NA None Various including:
Population, population density, percent elderly, none white, poverty levels, etc. No ~ 9 ---- Pope et al. AJRCCM 1995 Krewski et al. HEI 2000 ACS CPS-II cohort/ 1982-1989 Standard Cox proportional hazards model Age, Sex, Race smoking, education, marital status, BMI, alcohol, dust/fume exposure None No 7 (4-10) 12 (7-17) Pope et al. JAMA 2002 ACS CPS-II cohort/ 1982-1998 Random Effects Cox proportional hazards model Age, Sex, Race smoking, education, marital status, BMI, alcohol, occupation/ occupational exposure, diet None Yes 6 (2-11) 9 (3-16) Krewski et al. HEI 2009 ACS CPS-II cohort/ 1982-2000 Random Effects Cox proportional hazards model Age, Sex, Race smoking, education, marital status, BMI, alcohol, occupation/ occupational exposure, diet Poverty, income disparity, household income, unemployment,
none white, education, air conditioning—at two levels of spatial scale (Zip Code, Metro)
No 6 (4-8) 13 (10-16)
P ercent i ncreas e in mort al il y ri sk (95% C I) -10 0 10 20 30 40 50 60 70 80 90 100 110 120 180 190
All Cause CPD CVD IHD
S ix Ci ti es (Do c k er y et al 19 93 ; K rew s k i et al . 20 00 ; La de n et al . 20 08 ) S ix Ci ti es, M ed ic ar e (E fi m et al . 20 08 ) ACS ACS Osl o, m en an d w om en , 51 -70 ( Na ess et al . 20 07 ) ACS A HS M OG, M al es (M c Do nn el l et al . 20 00 ) V A , Hy pe rt en s iv e, M al es (Li pf er t et al . 20 06 ) 11 CA c ou nt y , el de rl y ( E nst rom 20 05 ) Fr en c h P A A RC ( Fi lleu l et al . 20 05 ) Du tc h Co ho rt ( B ee len et al . 20 08 ) S ix Ci ti es S ix Ci ti es A CS LA LA LA W om en 's He al th Ini ti at iv e (M ill er et al . 20 07 ) A HS M OG, Fem al e (Ch en et al . 20 05 ) Osl o, m en an d w om en , 71 -90 ( Na ess et al . 20 07 ) Ge m an w om en ( Ge hr ing et al . 20 06 ) U. S . M ed ic ar e; E ast /Ce nt ral /W est ( Zeg ar et al . 20 08 ) A CS M ed ic ar e (E fi m et al . 20 08 ) A HS M OG, M al es (M c Do nn el l et al . 20 00 ) Fr en c h P A A RC ( Fi lleu l et al . 20 05 ) Ge m an w om en ( Ge hr ing et al . 20 06 ) Du tc h Co ho rt ( B ee len et al . 20 08 ) Nu rs es' He al th S tud y ( P ue tt et al . 20 08 ) Nu rs es' He al th S tud y ( P ue tt et al . 20 08 ) P op e et al . 19 95 ; K rew s k i et al . 20 00 ; P op e et al . 20 02 , 20 04 ; J er ret t et al . 20 05 ; K rew s k i et al . 20 09 ) Ca l. T ea c he rs S tud y ( Ostr o et al . 20 09 ) Ca l. T ea c he rs S tud y ( Ostr o et al . 20 09 ) Ca l. T ea c he rs S tud y ( Ostr o et al . 20 09 )
Other cohort studies have shown associations between exposure
to fine PM and increased risk of cardiovascular death
.
Six-Cities studies ACS studies Other studies
P ercent i ncreas e in mort al il y ri sk (95% C I) -10 0 10 20 30 40 50 60 70 80 90 100 110 120 180 190
All Cause CPD CVD IHD
Joel Kaufman Lianne Sheppard
P ercent i ncreas e in mort al il y ri sk (95% C I) -10 0 10 20 30 40 50 60 70 80 90 100 110 120 180 190
All Cause CPD CVD IHD Lung Cancer
Nurses’ Health Study:
•Puett et al. Am. J. Epidemiology 2008 Stronger association with CVD than with all cause.
P ercent i ncreas e in mort al il y ri sk (95% C I) -10 0 10 20 30 40 50 60 70 80 90 100 110 120 180 190
All Cause CPD CVD IHD Lung Cancer
Netherlands, Germany, Norway studies: Beelen et al. EHP 2008
Gehring et al. Epidemiology 2006
Naess et al. Am. J. Epidemiology 2007 Again, positive associations, generally Stronger for cardiovascular disease. Brunekreef (summary paper)
JESEE 2007
P ercent i ncreas e in mort al il y ri sk (95% C I) -10 0 10 20 30 40 50 60 70 80 90 100 110 120 180 190
All Cause CPD CVD IHD
U.S. Medicare Cohort studies:
•Eftim et al. Epidemiology 2008 •Zegar et al. EHP 2008
Cohorts of Medicare participants cities of the 6-cities and ACS study, plus all U.S.
Age 0 5 10 15 20 25 30 35 40 45 50 55 60 65 70 75 80 85 90 95 100 105 S urv iv al P robabilit y 0 10 20 30 40 50 60 70 80 90 100
Baseline survival curve, life expect.=76.4
1.25 RR from Pollut, ages < 45 unaffected; life expect.=73.9 1.25 RR from Pollut., infants unaffected; life expect.=73.5 1.25 RR from Pollut., infants affected; life expect. = 73.4 2.00 RR from Smoking from age 20; life expect.=67.9
Survival curves based on projected U.S life tables and alternative excess risk assumptions
Note: 1.15 RR from Polut., infants uneffected; life expect=74.6 (curve not shown)
Pope 2000 Brunekreef 1997
Brief methodological outline of air
pollution epidemiological studies:
Studies of short-term exposure
Episode
Population-based daily time-series
Panel-based acute exposure
Case-crossover
Studies of long-term exposure
Population-based cross-sectional
Cohort-based mortality
Cohort- and panel-based morbidity
Case-control studies
Intervention/natural experiment
Exploit temporal variability Exploit spatial variability Exploit both temporal and spatial variabilitySouthern California Children’s Health Study
Effects of air pollution on
children’s health, especially
lung function growth.
David Bates, Advisor
Southern California Children’s Health Study, has shown that
air pollution impacts lung development in children.
Children living in cities with higher air pollution and living near major traffic sources showed greater deficits in lung function growth.
Brief methodological outline of air
pollution epidemiological studies:
Studies of short-term exposure
Episode
Population-based daily time-series
Panel-based acute exposure
Case-crossover
Studies of long-term exposure
Population-based cross-sectional
Cohort-based mortality
Cohort- and panel-based morbidity
Case-control studies
Intervention/natural experiment
Exploit temporal variability Exploit spatial variability Exploit both temporal and spatial variabilitySteubenville Topeka Watertown Kingston St. Louis Portage
Reduction in fine particulate air pollution:
Extended follow-up of the Harvard Six Cities Study
Laden, Schwartz, Speizer, Dockery, 2006
Follow up analysis of the Six-Cities cohort:
Copper Smelter Strike, Mid July 1967 – March 1968
Adapted from: Trijonis, John. Atmospheric Environment 1979
Age 0 5 10 15 20 25 30 35 40 45 50 55 60 65 70 75 80 85 90 95 100 105 S urv iv al P robabilit y 0 10 20 30 40 50 60 70 80 90 100
Baseline survival curve, life expect.=76.4
1.25 RR from Pollut, ages < 45 unaffected; life expect.=73.9 1.25 RR from Pollut., infants unaffected; life expect.=73.5 1.25 RR from Pollut., infants affected; life expect. = 73.4 2.00 RR from Smoking from age 20; life expect.=67.9
Survival curves based on projected U.S life tables and alternative excess risk assumptions
Note: 1.15 RR from Polut., infants uneffected; life expect=74.6 (curve not shown)
Pope 2000 Brunekreef 1997
- Matching PM2.5 data for 1979-1983 and 1999-2000 in 51 Metro Areas
- Life Expectancy data for 1978-1982 and 1997-2001 in 211 counties in 51 Metro areas - Evaluate changes in Life
Expectancy with changes in
PM2.5 for the 2-decade period
of approximately 1980-2000.
Fine-Particulate Air Pollution and Life Expectancy in the United States
C. Arden Pope, III, Ph.D., Majid Ezzati, Ph.D., and Douglas W. Dockery, Sc.D.
January 22, 2009
Do cities with bigger improvements in air quality have bigger
improvements in health, measured by life expectancy?
Covariates included in the regression models
Changes in socio-economic and demographic variables (from U.S. Census Data):
Per capita income
Population
5-yr in-migration
High-school graduates
Urban population
Black proportion of population
Hispanic proportion of population
Proxy cigarette smoking variables—available for all 211 counties
COPD mortality rates
Lung Cancer mortality rates
Survey-based metro-area estimates of smoking prevalence National Health Interview Survey (1978-1980)
Behavioral Risk Factor Surveillance System (1998-2000)
Clustered standard errors (clustered by the 51 metro areas) were estimated for all models except for analysis that included only the 51 largest counties in each metro area.
A 10 µg/m
3decrease in PM
2.5was associated with
a
7.3 (± 2.4) month
increase in life expectancy.
This increase in life expectancy persisted even after controlling for socio-economic, demographic, or smoking variables
Reduction in PM2.5, 1980-2000 0 2 4 6 8 10 12 14 Chan g e in LE , 19 80 s - 1 99 0s 0.0 0.5 1.0 1.5 2.0 2.5 3.0 3.5 4.0 4.5 5.0 5.5 22 47 49 45 4 10 17 19 46 48 6 43 50 24 21 36 8 34 20 7 25 1 11 12 14 44 51 27 3 28 30 32 13 18 26 9 29 23 37 38 40 15 33 5 2 35 31 16 39 41 42 Reduction in PM2.5, 1980-2000 0 2 4 6 8 10 12 14 Residual changes in LE cont rollin g f or cov ariat es -2.5 -2.0 -1.5 -1.0 -0.5 0.0 0.5 1.0 1.5 2.0 2.5 22 47 49 45 4 10 17 19 46 48 6 43 50 24 21 36 8 34 20 7 25 1 11 12 14 44 51 27 3 28 30 32 13 18 26 9 29 23 37 38 40 15 33 5 2 35 31 16 39 41 42
A
B
Air Pollution Reduction:
Is it Real and Does it Work?
Yes