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The global atmospheric environment for the next generation

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The global atmospheric environment for the next generation. / Dentener, F ; Stevenson, D ; Ellingsen, K et al.
In: Environmental Science and Technology, Vol. 40, No. 11, 01.06.2006, p. 3586-3594.

Research output: Contribution to Journal/MagazineJournal articlepeer-review

Harvard

Dentener, F, Stevenson, D, Ellingsen, K, van Noije, T, Schultz, M, Amann, M, Atherton, C, Bell, N, Bergmann, D, Bey, I, Bouwman, L, Butler, T, Cofala, J, Collins, B, Drevet, J, Doherty, R, Eickhout, B, Eskes, H, Fiore, A, Gauss, M, Hauglustaine, D, Horowitz, L, Isaksen, ISA, Josse, B, Lawrence, M, Krol, M, Lamarque, JF, Montanaro, V, Muller, JF, Peuch, VH, Pitari, G, Pyle, J, Rast, S, Rodriguez, J, Sanderson, M, Savage, NH, Shindell, D, Strahan, S, Szopa, S, Sudo, K, Van Dingenen, R, Wild, O & Zeng, G 2006, 'The global atmospheric environment for the next generation', Environmental Science and Technology, vol. 40, no. 11, pp. 3586-3594. https://doi.org/10.1021/es0523845

APA

Dentener, F., Stevenson, D., Ellingsen, K., van Noije, T., Schultz, M., Amann, M., Atherton, C., Bell, N., Bergmann, D., Bey, I., Bouwman, L., Butler, T., Cofala, J., Collins, B., Drevet, J., Doherty, R., Eickhout, B., Eskes, H., Fiore, A., ... Zeng, G. (2006). The global atmospheric environment for the next generation. Environmental Science and Technology, 40(11), 3586-3594. https://doi.org/10.1021/es0523845

Vancouver

Dentener F, Stevenson D, Ellingsen K, van Noije T, Schultz M, Amann M et al. The global atmospheric environment for the next generation. Environmental Science and Technology. 2006 Jun 1;40(11):3586-3594. doi: 10.1021/es0523845

Author

Dentener, F ; Stevenson, D ; Ellingsen, K et al. / The global atmospheric environment for the next generation. In: Environmental Science and Technology. 2006 ; Vol. 40, No. 11. pp. 3586-3594.

Bibtex

@article{6a324cd900d94974a9b67a34cf966b6c,
title = "The global atmospheric environment for the next generation",
abstract = "Air quality, ecosystem exposure to nitrogen deposition, and climate change are intimately coupled problems: we assess changes in the global atmospheric environment between 2000 and 2030 using 26 state-of-the-art global atmospheric chemistry models and three different emissions scenarios. The first (CLE) scenario reflects implementation of current air quality legislation around the world, while the second (MFR) represents a more optimistic case in which all currently feasible technologies are applied to achieve maximum emission reductions. We contrast these scenarios with the more pessimistic IPCC SRES A2 scenario. Ensemble simulations for the year 2000 are consistent among models and show a reasonable agreement with surface ozone, wet deposition, and NO2 satellite observations. Large parts of the world are currently exposed to high ozone concentrations and high deposition of nitrogen to ecosystems. By 2030, global surface ozone is calculated to increase globally by 1.5 +/- 1.2 ppb (CLE) and 4.3 +/- 2.2 ppb (A2), using the ensemble mean model results and associated +/- 1 sigma standard deviations. Only the progressive MFR scenario will reduce ozone, by -2.3 +/- 1.1 ppb. Climate change is expected to modify surface ozone by -0.8 +/- 0.6 ppb, with larger decreases over sea than over land. Radiative forcing by ozone increases by 63 +/- 15 and 155 +/- 37 mW m(-2) for CLE and A2, respectively, and decreases by -45 +/- 15 mW m(-2) for MFR. We compute that at present 10.1% of the global natural terrestrial ecosystems are exposed to nitrogen deposition above a critical load of 1 g N m(-2) yr(-1). These percentages increase by 2030 to 15.8% (CLE), 10.5% (MFR), and 25% (A2). This study shows the importance of enforcing current worldwide air quality legislation and the major benefits of going further. Nonattainment of these air quality policy objectives, such as expressed by the SRES-A2 scenario, would further degrade the global atmospheric environment.",
keywords = "NITROGEN DEPOSITION, TROPOSPHERIC OZONE, SURFACE OZONE, IMPACT, AFRICA",
author = "F Dentener and D Stevenson and K Ellingsen and {van Noije}, T and M Schultz and M Amann and C Atherton and N Bell and D Bergmann and I Bey and L Bouwman and T Butler and J Cofala and B Collins and J Drevet and R Doherty and B Eickhout and H Eskes and A Fiore and M Gauss and D Hauglustaine and L Horowitz and Isaksen, {I S A} and B Josse and M Lawrence and M Krol and Lamarque, {J F} and V Montanaro and Muller, {J F} and Peuch, {V H} and G Pitari and J Pyle and S Rast and J Rodriguez and M Sanderson and Savage, {N H} and D Shindell and S Strahan and S Szopa and K Sudo and {Van Dingenen}, R and O Wild and G Zeng",
year = "2006",
month = jun,
day = "1",
doi = "10.1021/es0523845",
language = "English",
volume = "40",
pages = "3586--3594",
journal = "Environmental Science and Technology",
issn = "0013-936X",
publisher = "American Chemical Society",
number = "11",

}

RIS

TY - JOUR

T1 - The global atmospheric environment for the next generation

AU - Dentener, F

AU - Stevenson, D

AU - Ellingsen, K

AU - van Noije, T

AU - Schultz, M

AU - Amann, M

AU - Atherton, C

AU - Bell, N

AU - Bergmann, D

AU - Bey, I

AU - Bouwman, L

AU - Butler, T

AU - Cofala, J

AU - Collins, B

AU - Drevet, J

AU - Doherty, R

AU - Eickhout, B

AU - Eskes, H

AU - Fiore, A

AU - Gauss, M

AU - Hauglustaine, D

AU - Horowitz, L

AU - Isaksen, I S A

AU - Josse, B

AU - Lawrence, M

AU - Krol, M

AU - Lamarque, J F

AU - Montanaro, V

AU - Muller, J F

AU - Peuch, V H

AU - Pitari, G

AU - Pyle, J

AU - Rast, S

AU - Rodriguez, J

AU - Sanderson, M

AU - Savage, N H

AU - Shindell, D

AU - Strahan, S

AU - Szopa, S

AU - Sudo, K

AU - Van Dingenen, R

AU - Wild, O

AU - Zeng, G

PY - 2006/6/1

Y1 - 2006/6/1

N2 - Air quality, ecosystem exposure to nitrogen deposition, and climate change are intimately coupled problems: we assess changes in the global atmospheric environment between 2000 and 2030 using 26 state-of-the-art global atmospheric chemistry models and three different emissions scenarios. The first (CLE) scenario reflects implementation of current air quality legislation around the world, while the second (MFR) represents a more optimistic case in which all currently feasible technologies are applied to achieve maximum emission reductions. We contrast these scenarios with the more pessimistic IPCC SRES A2 scenario. Ensemble simulations for the year 2000 are consistent among models and show a reasonable agreement with surface ozone, wet deposition, and NO2 satellite observations. Large parts of the world are currently exposed to high ozone concentrations and high deposition of nitrogen to ecosystems. By 2030, global surface ozone is calculated to increase globally by 1.5 +/- 1.2 ppb (CLE) and 4.3 +/- 2.2 ppb (A2), using the ensemble mean model results and associated +/- 1 sigma standard deviations. Only the progressive MFR scenario will reduce ozone, by -2.3 +/- 1.1 ppb. Climate change is expected to modify surface ozone by -0.8 +/- 0.6 ppb, with larger decreases over sea than over land. Radiative forcing by ozone increases by 63 +/- 15 and 155 +/- 37 mW m(-2) for CLE and A2, respectively, and decreases by -45 +/- 15 mW m(-2) for MFR. We compute that at present 10.1% of the global natural terrestrial ecosystems are exposed to nitrogen deposition above a critical load of 1 g N m(-2) yr(-1). These percentages increase by 2030 to 15.8% (CLE), 10.5% (MFR), and 25% (A2). This study shows the importance of enforcing current worldwide air quality legislation and the major benefits of going further. Nonattainment of these air quality policy objectives, such as expressed by the SRES-A2 scenario, would further degrade the global atmospheric environment.

AB - Air quality, ecosystem exposure to nitrogen deposition, and climate change are intimately coupled problems: we assess changes in the global atmospheric environment between 2000 and 2030 using 26 state-of-the-art global atmospheric chemistry models and three different emissions scenarios. The first (CLE) scenario reflects implementation of current air quality legislation around the world, while the second (MFR) represents a more optimistic case in which all currently feasible technologies are applied to achieve maximum emission reductions. We contrast these scenarios with the more pessimistic IPCC SRES A2 scenario. Ensemble simulations for the year 2000 are consistent among models and show a reasonable agreement with surface ozone, wet deposition, and NO2 satellite observations. Large parts of the world are currently exposed to high ozone concentrations and high deposition of nitrogen to ecosystems. By 2030, global surface ozone is calculated to increase globally by 1.5 +/- 1.2 ppb (CLE) and 4.3 +/- 2.2 ppb (A2), using the ensemble mean model results and associated +/- 1 sigma standard deviations. Only the progressive MFR scenario will reduce ozone, by -2.3 +/- 1.1 ppb. Climate change is expected to modify surface ozone by -0.8 +/- 0.6 ppb, with larger decreases over sea than over land. Radiative forcing by ozone increases by 63 +/- 15 and 155 +/- 37 mW m(-2) for CLE and A2, respectively, and decreases by -45 +/- 15 mW m(-2) for MFR. We compute that at present 10.1% of the global natural terrestrial ecosystems are exposed to nitrogen deposition above a critical load of 1 g N m(-2) yr(-1). These percentages increase by 2030 to 15.8% (CLE), 10.5% (MFR), and 25% (A2). This study shows the importance of enforcing current worldwide air quality legislation and the major benefits of going further. Nonattainment of these air quality policy objectives, such as expressed by the SRES-A2 scenario, would further degrade the global atmospheric environment.

KW - NITROGEN DEPOSITION

KW - TROPOSPHERIC OZONE

KW - SURFACE OZONE

KW - IMPACT

KW - AFRICA

U2 - 10.1021/es0523845

DO - 10.1021/es0523845

M3 - Journal article

VL - 40

SP - 3586

EP - 3594

JO - Environmental Science and Technology

JF - Environmental Science and Technology

SN - 0013-936X

IS - 11

ER -