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Evaluation of mortality changes associated with reduced wood smoke air pollution in Launceston, Australia
Fay Johnston, Menzies Institute for Medical Research, University of Tasmania
Ivan Hanigan, University of Tasmania
Sarah Henderson, British Columbia Center for Disease Control
Geoff Morgan, University of Sydney
Overview
• Background
• Air quality interventions
• The mortality evaluation
• Results
• Policy implications
Tasmania
Compared with the rest of Australia….
• Poorer
• Older
• Worse health
• More rural • more than half the live in small
rural towns
• More wood heating • Overall 30%
• 50% in smaller towns.
Launceston’s air quality and community responses 1990-2007
Problem identified
• Peak wood heater use • High community concern
Initial Responses
• Air Quality characterised in detail • Winter air quality forecasts • Planning of interventions
1990s 1994-2001 2001-2007
Coordinated Action
• Woodheater replacement program • Education and enforcement
Air pollution (PM10) in Launceston, 1994-2007
We compared mortality before and after the intervention
In central Launceston where the intervention took place (pop 66,000)
and
Central Hobart where there were no interventions (pop 147,000)
Exposure • Period of improved air quality (6 ½ years from July 2001) was
compared with the 6 ½ years before July 2001
Outcomes • Percent change in daily standardised all-cause, cardiovascular and
respiratory mortality
Analysis • Poisson time series regression adjusted for:
• Population age structure,
• influenza epidemics
• daily and lagged temperature and humidity
• day of week
• secular mortality trends in the rest of Tasmania - 150 day moving average of standardised daily mortality
Approach
Results – small numbers to work with
Mortality Annual
total Annual male
Annual female
Winter (male+female)
All cause 595 284 311 158
Cardiovascular 237 107 130 68
Respiratory 54 27 28 17
Mean annual number of deaths from all-causes, cardiovascular, and respiratory conditions in Launceston1994-2007
All-cause mortality and PM10, Launceston, 1994-2007
-30
-20
-10
0
10
20
30
40
Perc
ent
change
All-cause Cardiovascular Respiratory
Launceston
Hobart
-40
-30
-20
-10
0
10
20
30
Annual mortality
Winter mortality
Perc
ent
change
Mortality changes in Launceston and Hobart
Perc
ent
change
Launceston
Hobart
Annual mortality
Winter mortality
Perc
ent
change
Mortality changes in Launceston and Hobart - MALE
-40
-30
-20
-10
0
10
20
30
All-cause Cardiovascular Respiratory
-40
-30
-20
-10
0
10
20
30
Perc
ent
change
Launceston
Hobart
Annual mortality
Winter mortality
Perc
ent
change
Mortality changes in Launceston and Hobart - FEMALE
-40
-30
-20
-10
0
10
20
30
-30
-20
-10
0
10
20
30
40
All-cause Cardiovascular Respiratory
Mortality changes, Launceston and Hobart by age-group
Launceston
Hobart
-30
-20
-10
0
10
20
30
Age 60-74 years
Age 75+ years
-40
-30
-20
-10
0
10
20
30
All-cause Cardiovascular Respiratory
Perc
ent
change
Perc
ent
change
Sensitivity analyses
• Results robust to • Start date of ‘period of improved air quality’
• Definition of influenza epidemics
• Methods for age standardisation
• Modelling of metrological variables
• Results were sensitive to how we derived the secular trend from data for the rest of Tasmania
Sensitivity analysis: the influence of smoothing the data for secular long term and seasonal trends
all cause cardiovascular respiratory
Conclusions
• Coordinated interventions led to large sustained AQ improvement
• Improved AQ was associated with reduced mortality in Launceston but not in Hobart • Association clearest in men, especially 60 to 75 year age group • Trend towards reduced winter cardiovascular and respiratory mortality
Tasmania
• The local case study was influential – biomass smoke top priority in Australia’s most recent National Air Strategy
• Removing wood as a heating source was effective but is not widely supported • Wood heater use is increasing and many regret changing to electricity
• Renewable – forest resource
• How to reduce emissions? • Improve user technique
• Tighter emissions standards
• Simple technology
Implications for policy - Australian perspective
Implications for policy
• Longer term • Subsidise ultra-efficient - foolproof biomass
heaters
• Combine with forest and fire management
• Shorter term - strengthen regulation and health protection • Resource local councils / EPAs
• Better public education
• Better use of evidence-based interventions • Portable air cleaners
Thank you Hosts
• BC Lung Association
• Ryan Allen
Funding agencies • Australian Research Council
• Department of Health and Human Services Tasmania
Advice on original paper • Mark Clements
• Doug Dockery
• John Todd
• Mike Power
• John Innis
• EPA Tasmania
Model
log(Oij) = Period + Agej + Ti + Ti-2 + Hi + Hi-2 + DOWi + Flui + SecularTrend +
offset(log(Popij)) Oij = observed number of cases on dayi in Agej;
Period = indicator variable for pre- and post-intervention periods;
Age = age groups by 15 year intervals to age 74, then 5 year intervals to 84, and ages 85 years and older;
Ti = daily mean temperature (°C); T i -2 = average of 3-day lagged temperature dayi (°C);
Hi = daily mean dew point (°C); Hi-2 = average of 3-day lagged dew point (°C);
Flu = indicator variable for days when the 14-day moving average of deaths for influenza and pneumonia in Tasmania exceeded the 95th percentile;
SecularTrend = the 150-day moving average of the daily directly standardised cause-specific mortality rates for Tasmania (excluding the intervention population of Launceston);
Popij = interpolated population on dayi in Agej.
Model comparisons
Annual deaths per 100,000 people
1994-2000 2001-2007 Percent decrease
All Tasmania All-causes 833 712 14.61
Cardiovascular 373 265 28.91
Respiratory 78 62 20.50
Launceston All-cause 857 742 13.45
Cardiovascular 388 274 29.53
Respiratory 86 064 24.63
Hobart All-cause 825 722 12.48
Cardiovascular 358 268 25.18
Respiratory 76 64 15.73
Mortality in Tasmania 1994-200 and 2001-2007