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  • Payne et al. Frontiers 2017

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Nitrogen deposition and plant biodiversity: past, present, and future

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Nitrogen deposition and plant biodiversity: past, present, and future. / Payne, R.; Dise, Nancy B.; Field, C. et al.
In: Frontiers in Ecology and the Environment, Vol. 15, No. 8, 10.2017, p. 431-436.

Research output: Contribution to Journal/MagazineJournal articlepeer-review

Harvard

Payne, R, Dise, NB, Field, C, Dore, AJ, Caporn, SJM & Stevens, CJ 2017, 'Nitrogen deposition and plant biodiversity: past, present, and future', Frontiers in Ecology and the Environment, vol. 15, no. 8, pp. 431-436. https://doi.org/10.1002/fee.1528

APA

Payne, R., Dise, N. B., Field, C., Dore, A. J., Caporn, S. J. M., & Stevens, C. J. (2017). Nitrogen deposition and plant biodiversity: past, present, and future. Frontiers in Ecology and the Environment, 15(8), 431-436. https://doi.org/10.1002/fee.1528

Vancouver

Payne R, Dise NB, Field C, Dore AJ, Caporn SJM, Stevens CJ. Nitrogen deposition and plant biodiversity: past, present, and future. Frontiers in Ecology and the Environment. 2017 Oct;15(8):431-436. Epub 2017 Sept 5. doi: 10.1002/fee.1528

Author

Payne, R. ; Dise, Nancy B. ; Field, C. et al. / Nitrogen deposition and plant biodiversity : past, present, and future. In: Frontiers in Ecology and the Environment. 2017 ; Vol. 15, No. 8. pp. 431-436.

Bibtex

@article{b8ca1e2543f1480181ef5ecb843a840a,
title = "Nitrogen deposition and plant biodiversity: past, present, and future",
abstract = "Reactive nitrogen (N) deposition from intensive agricultural and industrial activity has been identified as the third greatest threat to global terrestrial biodiversity, after land-use and climate change. While the impacts of N deposition are widely acknowledged, their magnitude is poorly quantified. We combine N deposition models, empirical response functions, and vegetation mapping to simulate the effects of N deposition on plant species richness from 1900 to 2030, using the island of Great Britain as a case study. We find that current species richness values – when averaged across five widespread habitat types – are approximately one-third less than without N deposition. Our results suggest that currently expected reductions in emissions will achieve no more than modest increases in species richness by 2030, and that emissions cuts based on habitat-specific “critical loads” may be an inefficient approach to managing N deposition for the protection of plant biodiversity. The effects of N deposition on biodiversity are severe and are unlikely to be quickly reversed.",
author = "R. Payne and Dise, {Nancy B.} and C. Field and Dore, {A. J.} and Caporn, {Simon J. M.} and Stevens, {Carly Joanne}",
note = "Copyright by the Ecological Society of America",
year = "2017",
month = oct,
doi = "10.1002/fee.1528",
language = "English",
volume = "15",
pages = "431--436",
journal = "Frontiers in Ecology and the Environment",
issn = "1540-9295",
publisher = "ECOLOGICAL SOC AMER",
number = "8",

}

RIS

TY - JOUR

T1 - Nitrogen deposition and plant biodiversity

T2 - past, present, and future

AU - Payne, R.

AU - Dise, Nancy B.

AU - Field, C.

AU - Dore, A. J.

AU - Caporn, Simon J. M.

AU - Stevens, Carly Joanne

N1 - Copyright by the Ecological Society of America

PY - 2017/10

Y1 - 2017/10

N2 - Reactive nitrogen (N) deposition from intensive agricultural and industrial activity has been identified as the third greatest threat to global terrestrial biodiversity, after land-use and climate change. While the impacts of N deposition are widely acknowledged, their magnitude is poorly quantified. We combine N deposition models, empirical response functions, and vegetation mapping to simulate the effects of N deposition on plant species richness from 1900 to 2030, using the island of Great Britain as a case study. We find that current species richness values – when averaged across five widespread habitat types – are approximately one-third less than without N deposition. Our results suggest that currently expected reductions in emissions will achieve no more than modest increases in species richness by 2030, and that emissions cuts based on habitat-specific “critical loads” may be an inefficient approach to managing N deposition for the protection of plant biodiversity. The effects of N deposition on biodiversity are severe and are unlikely to be quickly reversed.

AB - Reactive nitrogen (N) deposition from intensive agricultural and industrial activity has been identified as the third greatest threat to global terrestrial biodiversity, after land-use and climate change. While the impacts of N deposition are widely acknowledged, their magnitude is poorly quantified. We combine N deposition models, empirical response functions, and vegetation mapping to simulate the effects of N deposition on plant species richness from 1900 to 2030, using the island of Great Britain as a case study. We find that current species richness values – when averaged across five widespread habitat types – are approximately one-third less than without N deposition. Our results suggest that currently expected reductions in emissions will achieve no more than modest increases in species richness by 2030, and that emissions cuts based on habitat-specific “critical loads” may be an inefficient approach to managing N deposition for the protection of plant biodiversity. The effects of N deposition on biodiversity are severe and are unlikely to be quickly reversed.

U2 - 10.1002/fee.1528

DO - 10.1002/fee.1528

M3 - Journal article

VL - 15

SP - 431

EP - 436

JO - Frontiers in Ecology and the Environment

JF - Frontiers in Ecology and the Environment

SN - 1540-9295

IS - 8

ER -