Production-based emissions, consumption-based emissions and consumption-based health impacts of PM2.5 carbonaceous aerosols in Asia

This study determined the production-based emissions, the consumption-based emissions, and the consumption-based health impact of primary carbonaceous aerosols (black carbon: BC, organic carbon: OC) in nine countries and regions in Asia (Indonesia, Malaysia, the Philippines, Singapore, Thailand, China, Taiwan, South Korea, and Japan) in 2008. For the production-based emissions, sectoral emissions inventory of BC and OC for the year of 2008 based on the Asian international input–output tables (AIIOT) was compiled including direct emissions from households. Then, a multiregional environmental input–output analysis with the 2008 AIIOT which was originally developed by updating the table of 2000 was applied for calculating the consumption-based emissions for each country and region. For the production-based emissions, China had the highest BC and OC emissions of 4520 Gg-C in total, which accounted for 75% of the total emissions in the nine countries and regions. For consumption-based emissions, China was estimated to have had a total of 4849 Gg-C of BC and OC emissions, which accounted for 77% of the total emissions in the Asia studied. We also quantified how much countries and regions induced emissions in other countries and regions. Furthermore, taking account of the source–receptor relationships of BC and OC among the countries and regions, we converted their consumption-based emissions into the consumption-based health impact of each country and region. China showed the highest consumption-based health impact of BC and OC totaling 111 × 103 premature deaths, followed by Indonesia, Japan, Thailand and South Korea. China accounted for 87% of the sum total of the consumption-based health impacts of the countries/regions, indicating that China's contribution to consumption-based health impact in Asia was greater than its consumption-based emissions. By elucidating the health impacts that each country and region had on other countries and from which country the impacts were received, we demonstrated that the characteristics of the consumption-based health impact varied significantly by country and region. We also determined the difference in the health impacts to other countries and regions due to the domestic final demand of each country and region, and the health impact due to the domestic final demand of that country or region.

[1]  Yuesi Wang,et al.  Estimation of emissions from field burning of crop straw in China , 2008 .

[2]  G. Powers,et al.  A Description of the Advanced Research WRF Version 3 , 2008 .

[3]  S. Davis,et al.  China’s international trade and air pollution in the United States , 2014, Proceedings of the National Academy of Sciences.

[4]  D. Byun,et al.  Review of the Governing Equations, Computational Algorithms, and Other Components of the Models-3 Community Multiscale Air Quality (CMAQ) Modeling System , 2006 .

[5]  E. Hertwich,et al.  Carbon footprint of nations: a global, trade-linked analysis. , 2009, Environmental science & technology.

[6]  M. Lenzen Consumer and producer environmental responsibility: A reply , 2008 .

[7]  H. Akimoto,et al.  An Asian emission inventory of anthropogenic emission sources for the period 1980-2020 , 2007 .

[8]  E. Hertwich THE LIFE CYCLE ENVIRONMENTAL IMPACTS OF CONSUMPTION , 2011 .

[9]  Gang Yu,et al.  Polychlorinated dibenzo-p-dioxins and dibenzofurans emissions from open burning of crop residues in China between 1997 and 2004. , 2008, Environmental pollution.

[10]  Douglas Crawford-Brown,et al.  Mapping flows of embodied emissions in the global production system. , 2011, Environmental science & technology.

[11]  G. Peters From production-based to consumption-based national emission inventories , 2008 .

[12]  Hitoshi Sasaki,et al.  Interdependence of Production and Income in Asia-Pacific Economies: An International Input-Output Approach , 2007 .

[13]  Jesper Munksgaard,et al.  CO2 accounts for open economies: producer or consumer responsibility? , 2001 .

[14]  Rokuta Inaba,et al.  Estimates of Embodied Global Energy and Air-Emission Intensities of Japanese Products for Building a Japanese Input–Output Life Cycle Assessment Database with a Global System Boundary , 2012, Environmental science & technology.

[15]  G. Cao,et al.  Inventory of black carbon and organic carbon emissions from China , 2006 .

[16]  Michael Q. Wang,et al.  An inventory of gaseous and primary aerosol emissions in Asia in the year 2000 , 2003 .

[17]  中華人民共和国国家統計局 China statistical yearbook , 1988 .

[18]  Tami C. Bond,et al.  On the future of carbonaceous aerosol emissions , 2004 .

[19]  Manfred Lenzen,et al.  International trade drives biodiversity threats in developing nations , 2012, Nature.

[20]  Shigemi Kagawa,et al.  Characterization of economic requirements for a "carbon-debt-free country". , 2012, Environmental science & technology.

[21]  Manfred Lenzen,et al.  THE INS AND OUTS OF WATER USE – A REVIEW OF MULTI-REGION INPUT–OUTPUT ANALYSIS AND WATER FOOTPRINTS FOR REGIONAL SUSTAINABILITY ANALYSIS AND POLICY , 2011 .

[22]  Kjartan Steen-Olsen,et al.  Carbon, land, and water footprint accounts for the European Union: consumption, production, and displacements through international trade. , 2012, Environmental science & technology.

[23]  E. Hertwich,et al.  Affluence drives the global displacement of land use , 2013 .

[24]  Charles D. Bernholz,et al.  The United Nations Commodity Trade Statistics Database (UN Comtrade) , 2004 .

[25]  S. Davis,et al.  Consumption-based accounting of CO2 emissions , 2010, Proceedings of the National Academy of Sciences.

[26]  Manfred Lenzen,et al.  Aggregation (in-)variance of shared responsibility: A case study of Australia , 2007 .