Simulating changes in regional air pollution over the eastern United States due to changes in global and regional climate and emissions

American Geophysical Union (AGU) - Tập 109 Số D22 - 2004
Christian Hogrefe1, Barry Lynn2, Kevin Civerolo3, Jia‐Yeong Ku3, J. Rosenthal4, Cynthia Rosenzweig5, R. A. Goldberg5, Stuart R. Gaffin2, Kim Knowlton4, Patrick L. Kinney4
1Atmospheric Sciences Research Center, State University of New York at Albany, Albany, New York USA
2Center for Climate Systems Research Columbia Earth Institute of Columbia University, Columbia University New York New York USA
3New York State Department of Environmental Conservation Bureau of Air Quality Analysis and Research Albany New York USA
4Mailman School of Public Health, Columbia University, New York, New York, USA
5NASA Goddard Institute for Space Studies New York New York USA

Tóm tắt

To simulate ozone (O3) air quality in future decades over the eastern United States, a modeling system consisting of the NASA Goddard Institute for Space Studies Atmosphere‐Ocean Global Climate Model, the Pennsylvania State University/National Center for Atmospheric Research mesoscale regional climate model (MM5), and the Community Multiscale Air Quality model has been applied. Estimates of future emissions of greenhouse gases and ozone precursors are based on the A2 scenario developed by the Intergovernmental Panel on Climate Change (IPCC), one of the scenarios with the highest growth of CO2 among all IPCC scenarios. Simulation results for five summers in the 2020s, 2050s, and 2080s indicate that summertime average daily maximum 8‐hour O3 concentrations increase by 2.7, 4.2, and 5.0 ppb, respectively, as a result of regional climate change alone with respect to five summers in the 1990s. Through additional sensitivity simulations for the five summers in the 2050s the relative impact of changes in regional climate, anthropogenic emissions within the modeling domain, and changed boundary conditions approximating possible changes of global atmospheric composition was investigated. Changed boundary conditions are found to be the largest contributor to changes in predicted summertime average daily maximum 8‐hour O3 concentrations (5.0 ppb), followed by the effects of regional climate change (4.2 ppb) and the effects of increased anthropogenic emissions (1.3 ppb). However, when changes in the fourth highest summertime 8‐hour O3 concentration are considered, changes in regional climate are the most important contributor to simulated concentration changes (7.6 ppb), followed by the effect of increased anthropogenic emissions (3.9 ppb) and increased boundary conditions (2.8 ppb). Thus, while previous studies have pointed out the potentially important contribution of growing global emissions and intercontinental transport to O3 air quality in the United States for future decades, the results presented here imply that it may be equally important to consider the effects of a changing climate when planning for the future attainment of regional‐scale air quality standards such as the U.S. national ambient air quality standard that is based on the fourth highest annual daily maximum 8‐hour O3 concentration.

Từ khóa


Tài liệu tham khảo

10.1029/2002JD002688

10.1080/10473289.2003.10466316

10.1029/2000JD900227

10.1002/qj.49711247307

10.1029/1998GL900013

Byun D. W. andJ. K. S.Ching(Eds.) (1999) Science algorithms of the EPA Models‐3 Community Multiscale Air Quality Model (CMAQ) modeling system EPA/600/R‐99/030 U.S. Environ. Prot. Agency Off. of Res. and Dev. Washington D. C.

10.1046/j.1365-2486.1999.00273.x

10.1002/qj.49710343602

Farrell B. P., 1979, Adaptation in human subjects to the effects of inhaled ozone after repeated exposure, Am. Rev. Respir. Dis., 119, 725

10.1029/2001JD000982

10.1029/2002GL015601

10.1029/2003JD003855

Fiore A. M., 2003, A global perspective on air quality: Intercontinental transport and linkages with climate, Environ. Manage., 69, 13

10.1164/arrd.1980.121.3.431

10.1164/ajrccm.164.7.2010043

10.1175/1520-0450(1998)037<0961:MMAHOI>2.0.CO;2

10.1029/94JD00246

10.1029/JD094iD10p12925

Grell G. A., 1994, NCAR Technical Note

Hogrefe C. et al. (2003a) Modeling the impact of global climate and regional land use change on regional climate and air quality over the northeastern United States paper presented at26th International Technical Meeting on Air Pollution Modeling and its Application N. Atl. Treaty Organ./Com. on the Challenges of Mod. Soc. Istanbul Turk. May 26–30.

Hogrefe C., 2003, Climate change and ozone air quality over the eastern United States: A modeling study, Eos Trans. AGU, 84

10.1016/j.atmosenv.2004.02.033

10.1021/es034031g

10.1175/1520-0493(1996)124<2322:NBLVDI>2.0.CO;2

Intergovernmental Panel on Climate Change (IPCC), 2000, Special Report on Emissions Scenarios

Intergovernmental Panel on Climate Change (IPCC), 2001, Climate Change 2001: The Scientific Basis

10.1029/1999GL900450

10.1029/1999JD900204

10.1029/2000GL011996

10.1023/A:1011513603066

McCarthy J. J., 2001, Climate Change 2001: Impacts, Adaptation and Vulnerability

10.1029/2001JD001410

10.1029/97JD00237

10.1016/S1462-9011(98)00013-6

Prather M., 2001, Climate Change 2001: The Scientific Basis, 239

10.1029/2002GL016285

10.1080/07055900.1995.9649550

10.1016/S0040-1625(99)00100-6

10.1029/94JD02146

10.1175/1520-0477(2001)082<0945:AOEOTR>2.3.CO;2

10.1016/S0013-9351(05)80167-7

10.1175/1520-0469(1993)050<2107:FSINS>2.0.CO;2

10.1029/2002JD002945

U.S. Environmental Protection Agency(1994) User's guide to Mobile5 (Mobile source emission factor model) Rep. EPA/AA/TEB/94/01 Ann Arbor Mich.

U.S. Environmental Protection Agency(2004) The Ozone Report: Measuring Progress Through 2003 Rep. EPA 454/K‐04‐001 Research Triangle Park N. C.

10.1016/1352-2310(95)00146-P

10.1029/2000JD000123

10.1029/92JD00412

10.1029/2000JD900309