Early Tree Diversity and Composition Effects on Topsoil Chemistry in Young Forest Plantations Depend on Site Context

Ecosystems ◽  
2021 ◽  
Author(s):  
Els Dhiedt ◽  
Kris Verheyen ◽  
Pallieter De Smedt ◽  
Quentin Ponette ◽  
Lander Baeten
AMBIO ◽  
2015 ◽  
Vol 45 (1) ◽  
pp. 29-41 ◽  
Author(s):  
Kris Verheyen ◽  
Margot Vanhellemont ◽  
Harald Auge ◽  
Lander Baeten ◽  
Christopher Baraloto ◽  
...  

Oecologia ◽  
2014 ◽  
Vol 177 (2) ◽  
pp. 581-594 ◽  
Author(s):  
Timo Domisch ◽  
Leena Finér ◽  
Seid Muhie Dawud ◽  
Lars Vesterdal ◽  
Karsten Raulund-Rasmussen

PeerJ ◽  
2016 ◽  
Vol 4 ◽  
pp. e1806 ◽  
Author(s):  
Cecilia Cuatianquiz Lima ◽  
Constantino Macías Garcia

Secondary cavity nesting (SCN) birds breed in holes that they do not excavate themselves. This is possible where there are large trees whose size and age permit the digging of holes by primary excavators and only rarely happens in forest plantations, where we expected a deficit of both breeding holes and SCN species. We assessed whether the availability of tree cavities influenced the number of SCNs in two temperate forest types, and evaluated the change in number of SCNs after adding nest boxes. First, we counted all cavities within each of our 25-m radius sampling points in mature and young forest plots during 2009. We then added nest boxes at standardised locations during 2010 and 2011 and conducted fortnightly bird counts (January–October 2009–2011). In 2011 we added two extra plots of each forest type, where we also conducted bird counts. Prior to adding nest boxes, counts revealed more SCNs in mature than in young forest. Following the addition of nest boxes, the number of SCNs increased significantly in the points with nest boxes in both types of forest. Counts in 2011 confirmed the increase in number of birds due to the addition of nest boxes. Given the likely benefits associated with a richer bird community we propose that, as is routinely done in some countries, forest management programs preserve old tree stumps and add nest boxes to forest plantations in order to increase bird numbers and bird community diversity.


2002 ◽  
pp. 66-78
Author(s):  
Ja. P. Didukh ◽  
P. M. Ustimenko ◽  
Ju. R. Shelag-Sosonko ◽  
P. G. Pluta ◽  
I. A. Korotchenko

The complex cartography of the Khmelnitskaya APS 30-kilometer zone (the total area of 282.6 thousand ha) was carried out during the elaboration of project according to the MAGATE demands. The present geobotanical map of zone was created in the scale 1 : 100 000. The ecological-phytocoenotical (dominant) vegetation classification was taken as a basis of the map's legend. The legend includes 27 numbers and 6 variants, represented by the boreal forest (11.6 % of area), nemoral forests (8.4 %), meadows (2.4 %), hydrophyte communities (3.2 %), agro- and urbo-communities (61.9 %) and young forest plantations (4.4 %). The characteristic of prevailing community types is given. Influence of the economic activity on the vegetation cover is shown. The geobotanical map can be used for both further monitoring and management of the forest economy with the aim of increasing the ecosystems stability against the external influences.


Author(s):  
Micah Fern ◽  
Rebecca Barlow ◽  
Chris Slootmaker ◽  
John Kush ◽  
Stephanie Shwiff ◽  
...  

Ecography ◽  
2018 ◽  
Vol 41 (11) ◽  
pp. 1776-1787 ◽  
Author(s):  
Suzanne T. S. van Beeck Calkoen ◽  
Dries P. J. Kuijper ◽  
Håkan Sand ◽  
Navinder J. Singh ◽  
Sip E. van Wieren ◽  
...  

2017 ◽  
Vol 78 (2) ◽  
pp. 179-186 ◽  
Author(s):  
Mateusz Marian Wolanin ◽  
Magdalena Natalia Wolanin ◽  
Krzysztof Oklejewicz

Abstract In forests of the Kolbuszowa Plateau, bramble thickets are common mainly in young forest plantations and clear-cut areas. 11 bramble species were found in 20 plantations visited during the field study. The most frequent bramble species in young forest plantations include: Rubus plicatus, R. nessensis, R. hirtus, R. idaeus, while less frequent are: R. gracilis, R. ambrosius and R. apricus. The largest patches of brambles were found in plantations established on sites of mixed pine-oak forest, subcontinental lime-oak-hornbeam forest and dried alder carrs. Rubus thickets in young forest plantations occur together with numerous species characteristic of communities classified into the following classes: Vaccinio-Piceetea, Querco-Fagetea, Epilobietea angustifolii, Molinio-Arrhenatheretea and Nardo-Callunetea. Brambles growing in young forest plantations can be roughly divided into three groups: I - species with thin, prostrate and rooting stems (R. hirtus, R. apricus, R. pedemontanus), which may significantly affect the growth of tree seedlings if bramble specimens or diaspores are present at the time of tree planting; II - species with strong, poorly branched and arcuate stems (R. plicatus, R. gracilis, R. ambrosius, R. glivicensis), whose negative effect on tree seedlings depends on the potential of a tree species to produce quickly a high and dense thicket thereby overshadowing the lower vegetation; III - species with erect and relatively sparsely growing stems (R. idaeus), which do not pose any threat to young forest plantations. Species with intermediate biological traits (e.g. R. nessensis) may have a negative impact on young plantations, as they generate large and dense bush, however, in most cases, their populations grow rather sparsely and do not hinder the development of tree seedlings.


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