Impact of Nitrogen Deposition on the Species Richness of Grasslands
By C. Stevens, N. Dise, J. Mountford, David Gowing. Science, 2004
1,520 citations recorded by the source corpus.
Subfields: Ecology, Nature and Landscape Conservation, Plant Science
View Paper: https://www.semanticscholar.org/paper/bb22fa40f54414a2a3747200d59bdc6781b574c8
How researchers see this paper
The researchers whose trusted networks rank it highest, strongest advocate first. Every researcher gets a different order.
In Ecology
- R. Bardgett
- R. Sinsabaugh
- K. Treseder
- Y. Kuzyakov
- David Tilman
- G. Grenouillet
- G. D. De Deyn
- S. Hobbie
In Nature and Landscape Conservation
In Plant Science
- R. Sinsabaugh
- Peter B. Reich
- S. Hobbie
- J. Levine
- Y. Kuzyakov
- K. Treseder
- Andrea Porras‐Alfaro
- B. Houlton
Citations in the corpus
- Global assessment of nitrogen deposition effects on terrestrial plant diversity: a synthesis. (2010, background): “Stevens et al. (2004) estimated a reduction of one species for every 2.5 kg N ha 1 yr 1 of N deposition, but also identify that this may be due to long-term cumulative deposition of N over decades, rather than current deposition.”
- Nitrogen additions and microbial biomass: a meta-analysis of ecosystem studies. (2008, background): “Plant community composition also frequently shifts, often towards species with greater litter quality (Chapin et al. 1986; Stevens et al. 2004; Suding et al. 2005).”
- The decline of moths in Great Britain: a review of possible causes (2013, background): “butterflies) correlates negatively with nitrogen input (Pollard et al., 1998; Stevens et al., 2004; Öckinger et al., 2006; WallisDeVries & van Swaay, 2006), so there may be substantial, unquantified impacts onmoth populations resulting from such chemical pollution.”
- Direct and productivity‐mediated indirect effects of fertilization, mowing and grazing on grassland species richness (2012, background): “The decrease in species richness of 37% (per 35 kg N per hectare and year) in Schwäbische Alb (the region with the most species-rich grasslands), 13% in Hainich-Dün, and 5% in Schorfheide-Chorin are similar to results in Stevens et al. (2004).”
- Effect of long-term nitrogen fertilization on mycorrhizal fungi associated with a dominant grass in a semiarid grassland (2007, background): “Nitrogen enrichment experiments have shown that increased N availability can significantly change the richness and composition of plant and fungal communities (Erland and Taylor 2002; Stevens et al. 2004).”
- Interactive effects of habitat modification and species invasion on native species decline. (2007, neutral): “Meeting this objective will demand more than the current focus on the independent effects of land-use change [4] ,a tmospheric CO2increase[5],climatechange[6],anthropogenicnitrogen deposition[ 7 ]andincreasingbioticexchange[8].Itisbecoming clear that the impact of one global change driver (see Gloss”
- Ecological impacts of early 21st century agricultural change in Europe--a review. (2009, background): “High fertilisation levels, regular re-seeding, and frequent mowing or intensive rotational grazing have led to a dramatic decline of grassland biodiversity (Stevens et al., 2004; Kahmen and Poschlod, 2008 for plants; Verhulst et al., 2004 for birds, Wenzel et al., 2006 for butterflies).”
- The Park Grass Experiment 1856–2006: its contribution to ecology (2006, background): “Such an effect has already been demonstrated for acid grasslands in the UK (Stevens et al. 2004).”
- Vegetation composition promotes carbon and nitrogen storage in model grassland communities of contrasting soil fertility (2009, background): “Retention of nutrients andwater are important ecosystems services which underpin sustainable productivity and diversity conservation (Stevens et al. 2004; Drinkwater & Snapp 2007; Schlesinger 2009).”