likhvar v 20150707_1700_upmc_jussieu_-_amphi_34
TRANSCRIPT
A multi-scale health impact assessment
of air pollution over the 21st century V. Likhvar, M. Pascal, K. Markakis, A. Colette, D. Hauglustaine, M. Valari,
S. Medina, P. Kinney
• Air pollution is a major health risks throughout the world
• adverse effects on human health throughout the lifespan
• action to reduce air pollution brings immediate and lasting
benefits for the health and well-being of the population
• How to assess the potential health impacts of air quality
policies?
• comparing air pollution policies and taking climate change into
account
• in a consistent way across scales
Background
Modeling framework
Global climate (World 2,5*1,25°)
[IPSLcm5A-MR]
Regional climate (Eur 0,44°)
[WRF]
Regional climate (Eur 0,11°)
[WRF]
Global chemistry (World 3,75*1,89°)
[INCA]
Regional chemistry (Eur 0,44°)
[CHIMERE]
Local chemistry (Eur 4 km)
[CHIMERE]
Present day,
RCP4.5
ECLIPSE CLE, MFR
Other scenario tested: Climate: RCP 2.6, RCP 8.5; Air pollution: GEEA
Health
Impact
Asessment
Health impact assessment
• Log-linear relationship bewteen
pollutant concentrations and
mortality
• Cardiovascular mortality / PM2,5
• Respiratory mortality /O3
• Comparison of future to present
impacts under different scenarios
• Health and population data
• 2008 annual mortality for 193
countries (WHO 2011)
• Gridded population over 15 years
old (Ciesin 2008, Insee 2009)
log(Mortality)
[Polluant]
Present
burden
Future
Scenario 1
Scenarios developed by the EU
commisison in 2013
- CLE: current legislation is applied
everywhere
- MFR: maximum feasible reduction,
using only technological solutions
Hypotheses for Europe: end of the economic crisis,
increase of the service economy and of high added-
value industrien decrease of traditionnal industry and
of agriculture
Energy efficiency; decrease by 10% the use of fossil
fuel in 2030
Estimate costs in Europe in 2030:
CLE 88.3 b€ per year
MFR 140.7 b€ per year
Air pollutants emissions
World - changes in PM2.5 2030 / 2010
CLE
MFR
World - Mortality impacts
• 2030 – CLE:
+ 6 800 cv deaths per year
• 2030 – MFR
-1.5 millions cv deaths per
year (84% in Asia)
- 0.82 millions deaths in China
- 0.24 millions deaths in India
Change in number of deaths due to
PM2,5 and ozone in 2030 compared to
2010 (per 100 000 inhab.)
Europe – PM2,5 related mortality
- 109 000 cv deaths per year - 219 000 cv deaths per year
Change in number of deaths due to PM2,5 in 2030
compared to 2010 (per 100 000 inhab.)
Europe – Ozone related mortality
- 4 800 resp deaths per year - 9 400 resp deaths per year
Change in number of deaths due to
ozone in 2030 compared to 2010
(per 100 000 inhab.)
Comparison across scales
Year Scenario
European countries at the
Global Scale (Ncountries = 38)
European countries at the
European Scale
(Ncountries = 38)
Conc.
range,
µg/m3
Avr.
change
in conc.,
µg/m3
Change
s in CV
deaths
Conc.
range,
µg/m3
Avr.
change
in conc.,
µg/m3
Changes
in CV
deaths
2030 CLE 0.5 - 5.7 -1.3 -55 099 2.2 - 9.0 -2.4 -109 398
MFR 0.5 - 4.8 -2.6 -105 356 2.0 - 7.5 -5 -218 843
IDF vs Europe: the estimates of the impacts of ozone changes on respiratory mortality
over Paris are15 time larger at the IdF scale than the European scale, under MFR.
Can we « correct » the results?
PM2.5 related CV deaths, CLE - 2030
Global scale Global scale
with
correction
European
scale
Europe -55 099 -108 900 -109 398
World + 6 600 + 329 000
• Large scale PM2,5- HIA is likely to be underestimated if no subgrid scale
correction is applied
• Better to work at the National or Regional scale
• City-specific impacts can only be assessed with a local scale model
Changes between 2030 and 2050
• PM2,5:
• few changes between 2030 and 2050
• scenarios assume that the vast majority of particle reduction
measures will already be in place by 2030.
• Ozone:
• increase in concentrations and resulting health impacts between
2030 and 2050,
• related to an increase in meteorological conditions conducive to
ozone formation.
Conclusions
• Implementing ambitious air quality policies would save
millions accross the world
• in 2050, the negative influence of climate on ozone could balance the
benefits of air quality policies targeting ozone
• More research is needed to better inform policies
• Modeling issues
• relevant scales for assessing impacts
• lack of consistent air pollution, climate and population scenarios
accross scales
• Health impact issues
• changes in the air pollution – mortality relationship?
• population growth should be taken into account
• other benefits should be taken into account
The project team
Victoria Likhvar, Didier Hauglustaine, Laboratoire des Sciences du Climat et de
l'Environnement (LSCE), Gif-sur-Yvette, France
Patrick Kinney, Department of Environmental Health Sciences, Columbia University in the
City of New York, Etats-Unis
Augustin Colette, Institut National de l’Environnement Industriel et des Risques, Ineris, Paris,
France
Myrto Valari, Konstandinos Markakis Laboratoire de Météorologie Dynamique (LMD), Institut
Pierre Simon Laplace (IPSL), Ecole Polytechnique, Palaiseau, France
Mathilde Pascal, Sylvia Medina, Département Santé Environnement, Institut de Veille
Sanitaire, InVS, Saint Maurice, France.
http://ac-hia.com/