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Published online 5 April 2007
Published in Soil Sci Soc Am J 71:720-729 (2007)
DOI: 10.2136/sssaj2006.0205
© 2007 Soil Science Society of America
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Soil and Plant Nitrogen Pools as Related to Plant Diversity in an Experimental Grassland

Yvonne Oelmanna,b,*, Wolfgang Wilckeb, Vicky M. Tempertonc, Nina Buchmannd, Christiane Roschere, Jens Schumachere, Ernst-Detlef Schulzee and Wolfgang W. Weisserf

a Inst. of Ecology, Dep. of Soil Science, Berlin Univ. of Technology, Salzufer 11-12, D-10587 Berlin, Germany
b Geographic Inst., Professorship of Soil Geography/Soil Science, Johannes Gutenberg Univ., Johann-Joachim-Becherweg 21, D-55128 Mainz, Germany
c Inst. of Chemistry and Dynamics of the Geosphere, ICGIII Phytosphere Inst., Jülich Research Centre, D-52425 Jülich, Germany
d Inst. of Plant Sciences, ETH Zentrum LFW C56, Universitätsstrasse 2, CH-8092 Zurich, Switzerland
e Max Planck Inst. for Biogeochemistry, P.O. Box 100164, D-07701 Jena, Germany
f Inst. of Ecology, Friedrich Schiller Univ. of Jena, Dornburger Straße 159, D-07743 Jena, Germany


Figure 1
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Fig. 1. Mean concentrations of NO3 in KCl extracts of the different sampling dates for plots (A) with and without legumes and plots (B) with and without grasses. Data are presented as mean ± standard error.

 

Figure 2
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Fig. 2. Relationship between species richness differentiated according to the presence of (A) legumes or (C) grasses, or functional group richness differentiated according to the presence (B) of legumes or (D) grasses, and concentrations of NO3 in KCl extracts in autumn 2003. Data are presented as mean ± standard error. Note that there is no 60-species mixture without legumes.

 

Figure 3
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Fig. 3. Relationship between species richness differentiated according to the presence of (A) legumes or (C) grasses, or functional group richness differentiated according to the presence of (B) legumes or (D) grasses, and volume-weighted mean (vwm) concentrations of dissolved organic N (DON) in spring 2003. Data are presented as mean ± standard error. Note that there is no 60-species mixture without legumes.

 

Figure 4
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Fig. 4. Relationship between species richness differentiated according to the respective sampling periods (A–C) and volume-weighted mean (vwm) concentrations of total dissolved N (TDN) and dissolved organic N (DON).

 

Figure 5
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Fig. 5. Relationship between species richness differentiated according to the presence of (A) legumes or (C) grasses, or functional group richness differentiated according to the presence of (B) legumes or (D) grasses, and volume-weighted mean (vwm) concentrations of total dissolved N (TDN) in spring 2003. Data are presented as mean ± standard error. Note that there is no 60-species mixture without legumes.

 

Figure 6
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Fig. 6. Relationship between species richness and mean N pools in plant mixture (aboveground) in May 2003 differentiated according to the presence of (A) legumes or (C) grasses, and functional group richness differentiated according to the presence of (B) legumes or (D) grasses. Data are presented as mean ± standard error. Note that there is no 60-species mixture without legumes.

 





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