James N. Galloway

James N. Galloway

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James N. Galloway


Research Focus & Metrics

Academic Career Length

51Years (1976-Present)

(Calculated once Scilit publication data is synced: current year − year of first publication + 1)

Representative Publications

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16 May 2008 in Science
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Journal Article
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JGJames N. Galloway
James N. Galloway
ATAlan R. Townsend
Alan R. Townsend
JEJan Willem Erisman
Jan Willem Erisman
MBMateete Bekunda
Mateete Bekunda
ZCZucong Cai
Zucong Cai
MSMark A. Sutton
Mark A. Sutton
Humans continue to transform the global nitrogen cycle at a record pace, reflecting an increased combustion of fossil fuels, growing demand for nitrogen in agriculture and industry, and pervasive inefficiencies in its use. Much anthropogenic nitrogen is lost to air, water, and land to cause a cascade of environmental and human health problems. Simultaneously, food production in some parts of the world is nitrogen-deficient, highlighting inequities in the distribution of nitrogen-containing fertilizers. Optimizing the need for a key human resource while minimizing its negative consequences requires an integrated interdisciplinary approach and the development of strategies to decrease nitrogen-containing waste.

28 May 2010 in Science
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Journal Article
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SBStuart H. M. Butchart
Stuart H. M. Butchart
MWMatt Walpole
Matt Walpole
BCBen Collen
Ben Collen
ASArco van Strien
Arco van Strien
JSJörn P. W. Scharlemann
Jörn P. W. Scharlemann
RWReg Watson
Reg Watson
Global Biodiversity Target Missed: In 2002, the Convention on Biological Diversity (CBD) committed to a significant reduction in the rate of biodiversity loss by 2010. There has been widespread conjecture that this target has not been met. Butchart et al. (p. 1164 , published online 29 April) analyzed over 30 indicators developed within the CBD's framework. These indicators include the condition or state of biodiversity (e.g., species numbers, population sizes), the pressures on biodiversity (e.g., deforestation), and the responses to maintain biodiversity (e.g., protected areas) and were assessed between about 1970 and 2005. Taken together, the results confirm that we have indeed failed to meet the 2010 targets.

28 September 2008 in Nature Geoscience
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Journal Article
Closed access
JEJan Willem Erisman
Jan Willem Erisman
MSMark A. Sutton
Mark A. Sutton
JGJames Galloway
James Galloway
ZKZbigniew Klimont
Zbigniew Klimont
WWWilfried Winiwarter
Wilfried Winiwarter

16 January 2008 in Nature
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Journal Article
Closed access
NGNicolas Gruber
Nicolas Gruber
JGJames N. Galloway
James N. Galloway

1 January 2003 in BioScience
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Journal Article
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JGJames N. Galloway
James N. Galloway
JAJohn D. Aber
John D. Aber
JEJan Willem Erisman
Jan Willem Erisman
SSSybil P. Seitzinger
Sybil P. Seitzinger
RHRobert W. Howarth
Robert W. Howarth
BCB. Jack Cosby
B. Jack Cosby
Human production of food and energy is the dominant continental process that breaks the triple bond in molecular nitrogen (N2) and creates reactive n

1 January 2010 in Ecological Applications
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Journal Article
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RBR. Bobbink
R. Bobbink
KHK. Hicks
K. Hicks
JGJ. Galloway
J. Galloway
TST. Spranger
T. Spranger
RAR. Alkemade
R. Alkemade
WVW. De Vries
W. De Vries
Atmospheric nitrogen (N) deposition is a recognized threat to plant diversity in temperate and northern parts of Europe and North America. This paper assesses evidence from field experiments for N deposition effects and thresholds for terrestrial plant diversity protection across a latitudinal range of main categories of ecosystems, from arctic and boreal systems to tropical forests. Current thinking on the mechanisms of N deposition effects on plant diversity, the global distribution of G200 ecoregions, and current and future (2030) estimates of atmospheric N‐deposition rates are then used to identify the risks to plant diversity in all major ecosystem types now and in the future.This synthesis paper clearly shows that N accumulation is the main driver of changes to species composition across the whole range of different ecosystem types by driving the competitive interactions that lead to composition change and/or making conditions unfavorable for some species. Other effects such as direct toxicity of nitrogen gases and aerosols, long‐term negative effects of increased ammonium and ammonia availability, soil‐mediated effects of acidification, and secondary stress and disturbance are more ecosystem‐ and site‐specific and often play a supporting role. N deposition effects in mediterranean ecosystems have now been identified, leading to a first estimate of an effect threshold. Importantly, ecosystems thought of as not N limited, such as tropical and subtropical systems, may be more vulnerable in the regeneration phase, in situations where heterogeneity in N availability is reduced by atmospheric N deposition, on sandy soils, or in montane areas.Critical loads are effect thresholds for N deposition, and the critical load concept has helped European governments make progress toward reducing N loads on sensitive ecosystems. More needs to be done in Europe and North America, especially for the more sensitive ecosystem types, including several ecosystems of high conservation importance.The results of this assessment show that the vulnerable regions outside Europe and North America which have not received enough attention are ecoregions in eastern and southern Asia (China, India), an important part of the mediterranean ecoregion (California, southern Europe), and in the coming decades several subtropical and tropical parts of Latin America and Africa. Reductions in plant diversity by increased atmospheric N deposition may be more widespread than first thought, and more targeted studies are required in low background areas, especially in the G200 ecoregions.