Deadwood specific density and its influential factors: A case study from a pure Norway spruce old-growth forest in the Eastern Carpathians

2012 ◽  
Vol 283 ◽  
pp. 77-85 ◽  
Author(s):  
Marius Teodosiu ◽  
Olivier B. Bouriaud
Keyword(s):  
Norway Spruce ◽  
Influential Factors ◽  
Old Growth ◽  
Specific Density ◽  
Old Growth Forest ◽  
Eastern Carpathians

scholarly journals Structural Features of Old Growth Forest from South Eastern Carpathians, Romania

2019 ◽  
Vol 10 (2) ◽  
pp. 159-164
Author(s):  
Valentin Cristea ◽  
Ștefan Leca ◽  
Albert Ciceu ◽  
Șerban Chivulescu ◽  
Ovidiu Badea
Keyword(s):  
Norway Spruce ◽  
Gini Index ◽  
Tree Height ◽  
European Beech ◽  
Structural Features ◽  
Distribution Functions ◽  
Old Growth ◽  
Old Growth Forest ◽  
Eastern Carpathians ◽  
Beech Stand

Background and Purpose: Romania’s forests are of globally significant value due to their natural characteristics, as similar forests in some other parts of the world have been lost forever. These types of forests, so-called "virgin" and "quasi-virgin (old growth)" forests, are also identified in the Buzau Mountains, which are part of the Eastern Carpathians in Romania (Curvature Region). Materials and Methods: To study and understand the structure and dynamics of primeval forest, four permanent one-hectare research plots were installed in the Penteleu Mountains, part of the Buzau Mountains. All trees with a diameter at breast height (DBH) greater than 80 mm were measured and their main dendrometric characteristics (DBH, height and social position) registered. The forest structure was analysed by fitting different theoretical distribution functions (beta, gamma, gamma 3P, gamma 3P mixt, loglogistic 3p, lognormal 3P and Weibull 3p). The structural homogeneity of the permanent research plots was tested using the Camino index (H) and Gini index (G). Results: For the smaller DBH categories, Norway spruce was relatively shorter in height, but with increasing DBH, the heights of Norway spruce exceeded those of European beech. Stand volume varied between 615 and 1133 m3 per hectare. The area of maximum stability where we encountered the lowest tree height variability was recorded between the 60 cm and 100 cm diameter categories. The Lorenz curve and the Gini index indicated that the studied stands have high structural biodiversity. Conclusions: The results showed that the studied forests have an optimal structural diversity, assuring them a higher stability and multifunctionality. Thus, these forests are models for managed forests.

Seven decades of change in a European old-growth forest following a stand-replacing wind disturbance: A long-term case study

2017 ◽  
Vol 399 ◽  
pp. 197-205 ◽  
Author(s):  
Peter Jaloviar ◽  
Milan Saniga ◽  
Stanislav Kucbel ◽  
Ján Pittner ◽  
Jaroslav Vencurik ◽  
...  
Keyword(s):  
Wind Disturbance ◽  
Old Growth ◽  
Old Growth Forest

Forest Reorganization: A Case Study in an Old-Growth Forest Catastrophic Blowdown

Ecology ◽  
1995 ◽  
Vol 76 (3) ◽  
pp. 763-774 ◽  
Author(s):  
Chris J. Peterson ◽  
Steward T. A. Pickett
Keyword(s):  
Old Growth ◽  
Old Growth Forest

How long do Norway spruce snags stand? Evaluating four estimation methods

2004 ◽  
Vol 34 (2) ◽  
pp. 376-383 ◽  
Author(s):  
Ken Olaf Storaunet ◽  
Jørund Rolstad
Keyword(s):  
Norway Spruce ◽  
Bark Beetles ◽  
Survival Function ◽  
Estimation Methods ◽  
Time Since Death ◽  
Calculation Methods ◽  
Old Growth ◽  
Standing Time ◽  
South Central ◽  
Old Growth Forest

We estimated time from death to fall (standing time) of Norway spruce (Picea abies (L.) Karst.) snags in a submountainous old-growth forest in south-central Norway, applying four calculation methods to 124 dendro chrono logically cross-dated still-standing snags and 64 fallen logs. The calculation methods consistently estimated expected standing time of snags at 26–34 years, with a median of 16–21 years and 20% of snags standing for >48–58 years. The survival function from all methods took the approximate form of a negative exponential, with a 3%–4% annual fall rate for snags. In the distribution of time since death, a small peak in dead trees 20–30 years ago (late 1970s) coincides with a historic epidemic of bark beetles. The method using only time since death of still-standing snags appears to be the most feasible for estimating total standing time of snags in old-growth forests with constant tree mortality.

scholarly journals The importance of managing and conserving large old trees: a case study from Victorian Mountain Ash forests

2016 ◽  
Vol 128 (1) ◽  
pp. 64 ◽  
Author(s):  
David Lindenmayer
Keyword(s):  
Key Management ◽  
Management Strategies ◽  
Population Recovery ◽  
Old Growth ◽  
Old Growth Forest ◽  
Eastern Australia ◽  
Mountain Ash ◽  
Old Trees ◽  
Regrowth Forest

Large old trees are critical structures in the Mountain Ash forests of the Central Highlands of Victoria. They perform many critical ecological and other roles. Populations of these trees are also in serious decline. A range of key management strategies is needed to arrest the decline of existing populations of large old trees and instigate population recovery. In particular all existing large old trees need to be properly protected with adequate buffers of uncut forest. In addition, all stands of old-growth forest, irrespective of their size, need to be protected to ensure they are not logged. The size of the old-growth estate also must be expanded so that it encompasses at least 30%‒50% of the distribution of Mountain Ash. Finally, the recruitment of new cohorts of large old trees is critically important to replace existing trees when they are lost. To achieve this, large areas of existing regrowth forest that regenerated after the 1939 fires need to be excluded from logging and grown through to an old-growth stage. Implementation of altered management in Mountain Ash forests is urgent, as delays in policies will exacerbate the decline of this significant population of large old trees in south-eastern Australia.

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