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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


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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

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Dose-response relationship Application of AIM/Material model (CGE) Application of AIM/Local model (bottom-up) GIS analysis (Idrisi Kilimanjaro)

The main topics

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What is air pollution?

Air pollution is the presence in the atmosphere

  • f a mix of chemicals and particles which is

harmful to human, animal and plant. Human health Human health

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What are the sources of air pollution?

Nature: volcanic eruption, forest fire…. Man-made:

  • combustion: fossil fuels, etc
  • non-combustion: production process, road dust……

Man Man-

  • made air pollution

made air pollution

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What are the components of air pollution?

Gaseity pollutants: SO2, NOx, CO, hydrocarbon Particulates: a mixture of solid particles and

liquid droplets which toxicity vary in size and composition

  • Composition:

Composition: Pb Pb, , Cd Cd, Ni, , Ni, Mn Mn, Fe, Al, Br, PAH , Fe, Al, Br, PAH… …

  • Carrier: gaseity pollutant,

Carrier: gaseity pollutant, microorganism microorganism

  • Size: aerodynamic diameter

Size: aerodynamic diameter

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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.

PM PM10

10 is the primary air pollutant in China at present

is the primary air pollutant in China at present

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Quantification of health effects

  • The way we test the health effects of air pollution is to watch the time trend of the

pollutants and see if it is similar to the time trend of health effects.

  • Selection of air pollution indicator: PM10 for China

Independent negative impact, no-harvesting, no threshold Reference: WHO guidelines for air quality

  • Selection of health outcomes
  • Sub-clinical health effects, lung function, immune function, low birth weight,

intelligence quotient, et al. are excluded

  • Quantitative dose-response relationship between air pollution and health effects

should have been established

  • Baseline disease data of the focused health effect in the target population should be

available

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Selected health outcomes associated with PM10 exposure in China

Non-accident mortality

  • Acute mortality
  • Chronic mortality

Morbidity

  • Hospital visit (internal medicine & pediatrics)
  • Hospital admission (respiratory, cardiovascular &

cerebrovascular)

  • Other diseases (acute upper respiratory tract infectious, chronic

bronchitis )

International Statistical Classification of Diseases International Statistical Classification of Diseases (ICD) (ICD)

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Dose-response relationship ) 1 ( − × × =

ΔC

e M POP E

β

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:

  • Local epidemiological studies are preferable
  • Meta analysis (mean and 95% CI): refer to the manual of STATA, SAS

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

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How to value health impacts

Two popular approaches in China

  • 1. Human capital approach

The market value of a premature death equals the discounted flows of earning in the future if he had not died.

  • 2. Contingent valuation approach

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

  • r illness.

Implications: economic burden of disease from the point of view of people Reference: National burden of disease studies: a practical guide. WHO, 2001.

  • 3. CGE model: health impacts on national economy
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Schematic Diagram of CGE model

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

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Impacts of labor loss and health service demand on the final consumption by commodities

  • 6.00
  • 4.00
  • 2.00

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

labor loss health service demand

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Impacts of health service demand on the output by sectors

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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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Structure of AIM/Material Model for health

Inclusion of SO2 and PM emissions as bi- products of economic activities in AIM/Material (data source: SEPA)

  • total amount constraint on SO2 and PM
  • impose SO2 tax

Household rural /urban

Final consumption Investment Labor and capital endowments

  • different problem of air pollution
  • change of energy structure in rural areas

rural/urban

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Schematic Diagram of Integrated Assessment

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

?

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Linkage between AIM/Material Model and AIM/Local Model

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Structure of AIM/Local Model of China

Sectors classification

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

  • n the projection on total
  • utput of commodities

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

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Data modification in AIM/Local model

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Emission map (vector)

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A-GIS

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

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Grid map of emission (raster, 30sec)

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GIS statistics (Idrisi)

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

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Health effects under the different scenarios

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(%)

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Thank You!