A project by Mikhail Chester and Professor Arpad Horvath of the University of California, Berkeley. This project was originally the dissertation work of Mikhail Chester. A project website has been created (www.sustainable-transportation.com) to report up-to-date information about the project.
Energy use and emission factors for passenger transportation modes typically ignore the total environmental inventory which includes vehicles, infrastructure, and fuel production components from design through end-of-life processes. A life-cycle inventory for each mode is necessary to appropriately address and attribute the transportation sector's energy and emissions impacts to reduction goals instead of allowing tailpipe factors to act as indicators of total system performance. To appropriately mitigate environmental impacts from transportation, it is necessary for decision makers to consider the life-cycle energy consumption and emissions associated with each mode. We created a comprehensive life-cycle energy, greenhouse gas emissions, and criteria air pollutant emissions inventory for the passenger transportation modes of automobiles, buses, rail, and airplanes in the U.S.. Each mode's inventory includes assessment of vehicles, infrastructure, and fuel components. For each component, analysis is performed from production (or construction) through use in both direct and indirect (supply chain) processes. We find that buses with peak-hour occupancies have the best energy and greenhouse gas performance, followed by rail and air systems, and trailed by automobiles. Air travel is not much worse than rail travel; in some cases even better. Off-peak bus travel is the worst performer. Inventorying criteria air pollutants yields a different ranking of transportation modes. Total life-cycle energy inputs and greenhouse gas emissions increase by 46% for onroad, 121% for rail, and 24% for air systems over vehicle tailpipe operation primarily due to vehicle manufacturing and maintenance, infrastructure construction, and fuel production. For criteria air pollutants, non-vehicle operational components often dominate total emissions. Per passenger mile traveled, total SO2 emissions are 24 times larger than operational emissions for automobiles. NOX emissions increase 64% for automobiles, up to 1280% for rail, and 21% for air. Non-tailpipe VOCs are 36% of total automobile and 79% of total rail and air emissions. Infrastructure and parking construction are major components of total PM10 emissions resulting in a large increase from vehicle operation for several modes. For rail and air systems, infrastructure construction and operation as well as vehicle manufacturing increase total CO emissions by 8 times from tailpipe performance.
