Integrated Assessment on Environmental Strategies & Health Impacts due to Air Pollution in China
Yue WAN Tokyo Institute of Technology APEIS Training Workshop NIES, 8 December 2004
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Integrated Assessment on Environmental Strategies & Health Impacts due to Air Pollution in China Yue WAN Tokyo Institute of Technology APEIS Training Workshop NIES, 8 December 2004 The main topics Dose-response relationship
Yue WAN Tokyo Institute of Technology APEIS Training Workshop NIES, 8 December 2004
Dose-response relationship Application of AIM/Material model (CGE) Application of AIM/Local model (bottom-up) GIS analysis (Idrisi Kilimanjaro)
Nature: volcanic eruption, forest fire…. Man-made:
Particulates less than 10um in diameter are most relevant to human health effects. They can penetrate anywhere within the respiratory tract beginning with the nasal passages to the alveoli, deep within the lungs according to diameter size.
10 is the primary air pollutant in China at present
pollutants and see if it is similar to the time trend of health effects.
Independent negative impact, no-harvesting, no threshold Reference: WHO guidelines for air quality
intelligence quotient, et al. are excluded
should have been established
available
Non-accident mortality
Morbidity
POP: : the exposed population M: baseline disease data of mortality or morbidity β: coefficient of dose-response relationship ∆C: change of pollutant concentration Source of β:
1. 1. Deaths by age groups Deaths by age groups 2. 2. Illness by age groups Illness by age groups 3. 3. Workday losses Workday losses 4. 4. Medical expenditure Medical expenditure
The market value of a premature death equals the discounted flows of earning in the future if he had not died.
It is based on the personal subjective responses rather than actual behavior that how much an individual is willing to pay to reduce the risk of dying
Implications: economic burden of disease from the point of view of people Reference: National burden of disease studies: a practical guide. WHO, 2001.
Dose-response relationship CGE model Capital Labor Energy Other inputs Production activity Goods 1 Goods m ... Air pollutants Increase of mortality Increase of illness Increase of health service demand Labor loss Concentration of pollutants* Household
consumption investment
$DEMAND:HOUSEHOLD Decrease in labor endowment Medical expenditure should be treated as negative endowment
0.00 2.00 4.00 6.00 8.00 10.00 12.00 14.00 16.00 18.00
AGR M_C M_G MIN FOD TEX W OD PAP OIL CHM NMP STL MET OHI OLI ELE HET GAS W TR T_F COM RES T_P HEL OSR
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labor loss health service demand
0.00 2.00 4.00 6.00 8.00 10.00 12.00 14.00 16.00
AGR M_C M_O M_G MIN FOD TEX WOD PAP OIL COL CHM NMP STL NFR MET ENV OHI REP OLI WST ELC ELO ELG ELH ELN ELB ELW ELP HET GAS WTR CNS T_F COM RES T_P HEL OSR
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Inclusion of SO2 and PM emissions as bi- products of economic activities in AIM/Material (data source: SEPA)
Household rural /urban
Final consumption Investment Labor and capital endowments
rural/urban
CGE Model
GIS
Air model
Population density map Emission inventory Population Exposure Pollution level
Health effects Environmental strategies Health effects
scenarios GIS D-R
GDP
National Economy
Power generation Cement production Steel production Nonferrous production Other industries Transport Commerce and service Urban household Rural household
Energy types
Raw Coal Briquette Coke Electricity Natural gas Crude oil Heavy oil Gasoline Kerosene Diesel oil LPG Town gas Heat Firewood
Database source : Energy Research Institute, China
Future demand is based
from AIM/Material Future demand is based on the projection on final consumption from AIM/Material
Future price is based on the projection from AIM/Material
Emission factors
combustion and non combustion process
Convert the results of AIM/Local to grid data that will be the input of air model Standard dataset: polygon map and grid map for Asia countries
Pollutant concentration in each grid (real number file) Reclass module Pollutant level in each grid (integer file) Population in each grid
Same reference system
Extract module Numbers of population expose to certain pollution level
Urban Rural Urban Rural Urban Rural Urban Rural 2000 3 3 3000 3000 2001 2 2 2000 2000 2002 1 1 1000 1000 2003 …… …… …… …… 2004 …… …… …… …… 2005 …… …… …… …… 2006 …… …… …… …… 2007 …… …… …… …… 2008 …… …… …… …… 2009 …… …… …… …… 2010 …… …… …… …… 2011 …… …… …… …… 2012 …… …… …… …… …… …… …… …… …… …… …… …… …… …… …… …… …… …… …… …… …… …… …… …… …… …… …… …… …… …… …… …… …… …… medical expenditure(yuan) Scenario 1 medical expenditure(yuan) rate of labor loss(%) BAU scenario rate of labor loss(%)