Biomass production and species composition change in a tallgrass prairie ecosystem after long‐term exposure to elevated atmospheric CO 2

1999 ◽  
Vol 5 (5) ◽  
pp. 497-506 ◽  
Author(s):  
Clenton E. Owensby ◽  
Jay. M. Ham ◽  
Alan. K. Knapp ◽  
Lisa. M. Auen
1993 ◽  
Vol 3 (4) ◽  
pp. 644-653 ◽  
Author(s):  
Clenton E. Owensby ◽  
Patrick I. Coyne ◽  
Jay M. Ham ◽  
Lisa M. Auen ◽  
Alan K. Knapp

2010 ◽  
Vol 17 (5) ◽  
pp. 1871-1883 ◽  
Author(s):  
LEON J. L. VAN DEN BERG ◽  
PHILIPPINE VERGEER ◽  
TIM C. G. RICH ◽  
SIMON M. SMART ◽  
DAN GUEST ◽  
...  

1994 ◽  
Vol 165 (1) ◽  
pp. 105-113 ◽  
Author(s):  
Clenton E. Owensby ◽  
Lisa M. Auen ◽  
Patrick I. Coyne

2015 ◽  
Vol 5 (3) ◽  
pp. 41-53
Author(s):  
Иванов ◽  
Sergey Ivanov ◽  
Коротков ◽  
Sergey Korotkov ◽  
Киселева ◽  
...  

Case studies of 75 permanent sample plots examine the directions of species composition change in different tree formations in case of normal evolution of biocoenoses and mass spruce decline. In case of natural development of forest biocoenoses, only on 5 plots of total 75 species composition of new tree generations is similar to that of the upper tree layer. On other 5 plots, the restoration of conditionally indigenous mixed spruce and lime forests proceeds. In all other cases, the forests develop towards the formation of broad-leaved communities with the predomination of lime. The expansion of maple in the undergrowth layer is observed on some plots. The change from spruce to lime forests is the most pronounced in the stands where the decline of spruce element occurred after bark beetle invasion.


2005 ◽  
Vol 33 (1) ◽  
pp. 251-254 ◽  
Author(s):  
Éva Lehoczky ◽  
András Kismányoky ◽  
Tamás Kismányoky

2012 ◽  
pp. 66-77 ◽  
Author(s):  
I. A. Lavrinenko ◽  
O. V. Lavrinenko ◽  
D. V. Dobrynin

The satellite images show that the area of marshes in the Kolokolkova bay was notstable during the period from 1973 up to 2011. Until 2010 it varied from 357 to 636 ha. After a severe storm happened on July 24–25, 2010 the total area of marshes was reduced up to 43–50 ha. The mean value of NDVI for studied marshes, reflecting the green biomass, varied from 0.13 to 0.32 before the storm in 2010, after the storm the NDVI decreased to 0.10, in 2011 — 0.03. A comparative analysis of species composition and structure of plant communities described in 2002 and 2011, allowed to evaluate the vegetation changes of marshes of the different topographic levels. They are fol­lowing: a total destruction of plant communities of the ass. Puccinellietum phryganodis and ass. Caricetum subspathaceae on low and middle marches; increasing role of halophytic species in plant communities of the ass. Caricetum glareosae vic. Calamagrostis deschampsioides subass. typicum on middle marches; some changes in species composition and structure of plant communities of the ass. Caricetum glareosae vic. Calamagrostis deschampsioides subass. festucetosum rubrae on high marches and ass. Parnassio palustris–Salicetum reptantis in transition zone between marches and tundra without changes of their syntaxonomy; a death of moss cover in plant communities of the ass. Caricetum mackenziei var. Warnstorfia exannulata on brackish coastal bogs. The possible reasons of dramatic vegetation dynamics are discussed. The dating of the storm makes it possible to observe the directions and rates of the succession of marches vegetation.


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