Environmental assessment of passenger
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To appropriately mitigate environmental impacts from transportation, it is necessary for
decision makers to consider the life-cycle energy use and emissions. Most current
decision-making relies on analysis at the tailpipe, ignoring vehicle production, infrastructure
provision, and fuel production required for support. We present results of a comprehensive
life-cycle energy, greenhouse gas emissions, and selected criteria air pollutant emissions
inventory for automobiles, buses, trains, and airplanes in the US, including vehicles...
Nội dung trích xuất từ tài liệu:
Environmental assessment of passenger IOP PUBLISHING ENVIRONMENTAL RESEARCH LETTERS Environ. Res. Lett. 4 (2009) 024008 (8pp) doi:10.1088/1748-9326/4/2/024008 Environmental assessment of passenger transportation should include infrastructure and supply chains Mikhail V Chester1 and Arpad Horvath Department of Civil and Environmental Engineering, University of California, 760 Davis Hall, Berkeley, CA 94720, USA E-mail: mchester@cal.berkeley.edu and horvath@ce.berkeley.edu Received 6 January 2009 Accepted for publication 5 May 2009 Published 8 June 2009 Online at stacks.iop.org/ERL/4/024008 Abstract To appropriately mitigate environmental impacts from transportation, it is necessary for decision makers to consider the life-cycle energy use and emissions. Most current decision-making relies on analysis at the tailpipe, ignoring vehicle production, infrastructure provision, and fuel production required for support. We present results of a comprehensive life-cycle energy, greenhouse gas emissions, and selected criteria air pollutant emissions inventory for automobiles, buses, trains, and airplanes in the US, including vehicles, infrastructure, fuel production, and supply chains. We find that total life-cycle energy inputs and greenhouse gas emissions contribute an additional 63% for onroad, 155% for rail, and 31% for air systems over vehicle tailpipe operation. Inventorying criteria air pollutants shows that vehicle non-operational components often dominate total emissions. Life-cycle criteria air pollutant emissions are between 1.1 and 800 times larger than vehicle operation. Ranges in passenger occupancy can easily change the relative performance of modes. Keywords: passenger transportation, life-cycle assessment, cars, autos, buses, trains, rail, aircraft, planes, energy, fuel, emissions, greenhouse gas, criteria air pollutants S Supplementary data are available from stacks.iop.org/ERL/4/024008 1. Background infrastructure provision and fuel production requirements to support these modes. Such is the case with CAFE and aircraft Passenger transportation’s energy requirements and emissions emission standards which target vehicle operation only [2, 3]. are receiving more and more scrutiny as concern for energy Recently, decision-making bodies have started to look to life- security, global warming, and human health impacts grows. cycle assessments (LCA) for critical inputs, typically related Passenger transportation is responsible for 20% of US energy to transportation fuels [4, 5]. In order to effectively mitigate consumption (approximately 5% of global consumption) and environmental impacts from transportation modes, life-cycle combustion emissions are strongly positively correlated [1]. environmental performance should be considered including The potentially massive impacts of securing petroleum both the direct and indirect processes and services required resources, climate change, human health, and equity issues to operate the vehicle. This includes raw materials extraction, associated with transportation emissions have accelerated manufacturing, construction, operation, maintenance, and end discussions about transportation environmental policy. of life of vehicles, infrastructure, and fuels. Decisions should Governmental policy has historically relied on energy and not be made based on partial data acting as indicators for whole emission analysis of automobiles, buses, trains, and aircraft at system performance. their tailpipe, ignoring vehicle production and maintenance, To date, a comprehensive LCA of passenger transportation 1 Author to whom any correspondence should be addressed. in the US has not been completed. Several studies and 1748-9326/09/024008+08$30.00 1 © 2009 IOP Publishing Ltd Printed in the UK Environ. Res. Lett. 4 (2009) 024008 M V Chester and A Horvath models analyze a single mode, particular externalities, or over the component’s lifetime (such as train station construc- specific phases, but none have performed a complete LCA tion) and are normalized appropriately. ...
Nội dung trích xuất từ tài liệu:
Environmental assessment of passenger IOP PUBLISHING ENVIRONMENTAL RESEARCH LETTERS Environ. Res. Lett. 4 (2009) 024008 (8pp) doi:10.1088/1748-9326/4/2/024008 Environmental assessment of passenger transportation should include infrastructure and supply chains Mikhail V Chester1 and Arpad Horvath Department of Civil and Environmental Engineering, University of California, 760 Davis Hall, Berkeley, CA 94720, USA E-mail: mchester@cal.berkeley.edu and horvath@ce.berkeley.edu Received 6 January 2009 Accepted for publication 5 May 2009 Published 8 June 2009 Online at stacks.iop.org/ERL/4/024008 Abstract To appropriately mitigate environmental impacts from transportation, it is necessary for decision makers to consider the life-cycle energy use and emissions. Most current decision-making relies on analysis at the tailpipe, ignoring vehicle production, infrastructure provision, and fuel production required for support. We present results of a comprehensive life-cycle energy, greenhouse gas emissions, and selected criteria air pollutant emissions inventory for automobiles, buses, trains, and airplanes in the US, including vehicles, infrastructure, fuel production, and supply chains. We find that total life-cycle energy inputs and greenhouse gas emissions contribute an additional 63% for onroad, 155% for rail, and 31% for air systems over vehicle tailpipe operation. Inventorying criteria air pollutants shows that vehicle non-operational components often dominate total emissions. Life-cycle criteria air pollutant emissions are between 1.1 and 800 times larger than vehicle operation. Ranges in passenger occupancy can easily change the relative performance of modes. Keywords: passenger transportation, life-cycle assessment, cars, autos, buses, trains, rail, aircraft, planes, energy, fuel, emissions, greenhouse gas, criteria air pollutants S Supplementary data are available from stacks.iop.org/ERL/4/024008 1. Background infrastructure provision and fuel production requirements to support these modes. Such is the case with CAFE and aircraft Passenger transportation’s energy requirements and emissions emission standards which target vehicle operation only [2, 3]. are receiving more and more scrutiny as concern for energy Recently, decision-making bodies have started to look to life- security, global warming, and human health impacts grows. cycle assessments (LCA) for critical inputs, typically related Passenger transportation is responsible for 20% of US energy to transportation fuels [4, 5]. In order to effectively mitigate consumption (approximately 5% of global consumption) and environmental impacts from transportation modes, life-cycle combustion emissions are strongly positively correlated [1]. environmental performance should be considered including The potentially massive impacts of securing petroleum both the direct and indirect processes and services required resources, climate change, human health, and equity issues to operate the vehicle. This includes raw materials extraction, associated with transportation emissions have accelerated manufacturing, construction, operation, maintenance, and end discussions about transportation environmental policy. of life of vehicles, infrastructure, and fuels. Decisions should Governmental policy has historically relied on energy and not be made based on partial data acting as indicators for whole emission analysis of automobiles, buses, trains, and aircraft at system performance. their tailpipe, ignoring vehicle production and maintenance, To date, a comprehensive LCA of passenger transportation 1 Author to whom any correspondence should be addressed. in the US has not been completed. Several studies and 1748-9326/09/024008+08$30.00 1 © 2009 IOP Publishing Ltd Printed in the UK Environ. Res. Lett. 4 (2009) 024008 M V Chester and A Horvath models analyze a single mode, particular externalities, or over the component’s lifetime (such as train station construc- specific phases, but none have performed a complete LCA tion) and are normalized appropriately. ...
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