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      Global soil nitrous oxide emissions since the preindustrial era estimated by an ensemble of terrestrial biosphere models: Magnitude, attribution, and uncertainty

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          An Earth-system perspective of the global nitrogen cycle.

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            Global patterns of plant leaf N and P in relation to temperature and latitude.

            A global data set including 5,087 observations of leaf nitrogen (N) and phosphorus (P) for 1,280 plant species at 452 sites and of associated mean climate indices demonstrates broad biogeographic patterns. In general, leaf N and P decline and the N/P ratio increases toward the equator as average temperature and growing season length increase. These patterns are similar for five dominant plant groups, coniferous trees and four angiosperm groups (grasses, herbs, shrubs, and trees). These results support the hypotheses that (i) leaf N and P increase from the tropics to the cooler and drier midlatitudes because of temperature-related plant physiological stoichiometry and biogeographical gradients in soil substrate age and then plateau or decrease at high latitudes because of cold temperature effects on biogeochemistry and (ii) the N/P ratio increases with mean temperature and toward the equator, because P is a major limiting nutrient in older tropical soils and N is the major limiting nutrient in younger temperate and high-latitude soils.
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              Is Open Access

              Nitrous oxide emissions from soils: how well do we understand the processes and their controls?

              Although it is well established that soils are the dominating source for atmospheric nitrous oxide (N2O), we are still struggling to fully understand the complexity of the underlying microbial production and consumption processes and the links to biotic (e.g. inter- and intraspecies competition, food webs, plant–microbe interaction) and abiotic (e.g. soil climate, physics and chemistry) factors. Recent work shows that a better understanding of the composition and diversity of the microbial community across a variety of soils in different climates and under different land use, as well as plant–microbe interactions in the rhizosphere, may provide a key to better understand the variability of N2O fluxes at the soil–atmosphere interface. Moreover, recent insights into the regulation of the reduction of N2O to dinitrogen (N2) have increased our understanding of N2O exchange. This improved process understanding, building on the increased use of isotope tracing techniques and metagenomics, needs to go along with improvements in measurement techniques for N2O (and N2) emission in order to obtain robust field and laboratory datasets for different ecosystem types. Advances in both fields are currently used to improve process descriptions in biogeochemical models, which may eventually be used not only to test our current process understanding from the microsite to the field level, but also used as tools for up-scaling emissions to landscapes and regions and to explore feedbacks of soil N2O emissions to changes in environmental conditions, land management and land use.
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                Author and article information

                Journal
                Global Change Biology
                Glob Change Biol
                Wiley
                13541013
                February 2019
                February 2019
                December 17 2018
                : 25
                : 2
                : 640-659
                Affiliations
                [1 ]International Center for Climate and Global Change Research, School of Forestry and Wildlife Sciences; Auburn University; Auburn Alabama
                [2 ]Research Center for Eco-Environmental Sciences; State Key Laboratory of Urban and Regional Ecology; Chinese Academy of Sciences; Beijing China
                [3 ]Department of Forestry; Mississippi State University; Mississippi State Mississippi
                [4 ]Department of Ecology, Evolution, and Organismal Biology; Iowa State University; Ames Iowa
                [5 ]Global Carbon Project; CSIRO Oceans and Atmosphere; Canberra Australia
                [6 ]Appalachian Laboratory; University of Maryland Center for Environmental Science; Frostburg Maryland
                [7 ]Department of Earth System Science; Woods Institute for the Environment, Stanford University; Stanford California
                [8 ]Precourt Institute for Energy; Stanford University; Stanford California
                [9 ]Karlsruhe Institute of Technology, Institute of Meteorology and Climate Research/Atmospheric Environmental Research; Garmisch-Partenkirchen Germany
                [10 ]Laboratoire des Sciences du Climat et de l'Environnement; LSCE; Gif sur Yvette France
                [11 ]IFAS, Soil and Water Sciences Department; University of Florida; Gainesville Florida
                [12 ]Center for Global Environmental Research; National Institute for Environmental Studies; Tsukuba Japan
                [13 ]Climate and Environmental Physics, Physics Institute; University of Bern; Bern Switzerland
                [14 ]Oeschger Centre for Climate Change Research; University of Bern; Bern Switzerland
                [15 ]Department of Physical Geography and Ecosystem Science; Lund University; Lund Sweden
                [16 ]Department of Biology Sciences; University of Quebec at Montreal (UQAM); Montréal Québec Canada
                [17 ]Department of Environmental Sciences; Emory University; Atlanta Georgia
                [18 ]Norsk Institutt for Luftforskning - NILU; Kjeller Norway
                [19 ]Air Quality and Greenhouse Gases (AIR); International Institute for Applied Systems Analysis; Laxenburg Austria
                [20 ]The Institute of Environmental Engineering, University of Zielona Gora; Zielona Gora Poland
                [21 ]Max Planck Institut für Biogeochemie; Jena Germany
                Article
                10.1111/gcb.14514
                30414347
                40ba0e43-5c23-4db5-be9f-08d4f306481f
                © 2018

                http://doi.wiley.com/10.1002/tdm_license_1.1

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