scholarly journals The Effects of a Western Spruce Budworm Outbreak on the Dead Wood Component in Relation to Ownership in Forests of Eastern Oregon

2010 ◽  
Vol 25 (4) ◽  
pp. 176-180 ◽  
Author(s):  
David Azuma

Abstract Forest Inventory and Analysis data were used to investigate the effects of a severe western spruce budworm outbreak on the dead wood component of forests in 11 counties of eastern Oregon for two time periods. The ownership and the level of damage (as assessed by aerial surveys) affected the resulting down woody material and standing dead trees. The pattern of coarse woody debris with respect to ownership and management intensity remained consistent into the next 10-year period. Harvesting tended to lower the amount of coarse woody debris on private forests. Federally managed forests had more standing dead trees than private lands, with more in the reserved than nonreserved areas. There was a reduction in the number of standing dead trees between the two periods.

2015 ◽  
Vol 76 (4) ◽  
pp. 322-330 ◽  
Author(s):  
Konrad Skwarek ◽  
Szymon Bijak

Abstract Dead wood plays an important role for the biodiversity of forest ecosystems and influences their proper development. This study assessed the amount of coarse woody debris in municipal forests in Warsaw (central Poland). Based on the forest site type, dominant tree species and age class, we stratified all complexes of the Warsaw urban forests in order to allocate 55 sample plots. For these plots, we determined the volume of dead wood including standing dead trees, coarse woody debris and broken branches as well as uprooted trees. We calculated the amount of dead wood in the distinguished site-species-age layers and for individual complexes. The volume of dead matter in municipal forests in Warsaw amounted to 38,761 m3, i.e. 13.7 m3/ha. The obtained results correspond to the current regulations concerning the amount of dead organic matter to be left in forests. Only in the Las Bielański complex (northern Warsaw) volume of dead wood is comparable to the level observed in Polish national parks or nature reserves, which is still far lower than the values found for natural forests. In general, municipal forests in Warsaw stand out positively in terms of dead wood quantity and a high degree of variation in the forms and dimensions of dead wood.


Author(s):  
O. Furdychko ◽  
◽  
O. Chornobrov ◽  
I. Solomakha ◽  
I. Tymochko ◽  
...  

Dead wood is an important component of forest ecosystems. It performs a number of environmental functions. Coarse woody debris includes standing dead trees, fallen dead trees, fragments of fallen trees (trunks), branches (fragments of branches), and rough tree roots. It is a substrate and habitat for living organisms, including a number of species of mosses, lichens, fungi, invertebrates, as well as birds and mammals. Woody detritus plays an important role in the biological cycle of substances and energy, and carbon deposition, is a source of nutrients. Therefore, the study of quantitative and qualitative features of dead wood, in particular on protected areas, is a considerable nowadays problem. The aim of the work is to estimate identified by forest inventory stocks of dead wood in forest ecosystems of Slobozhansky NNP by categories, as well as to analyze the distribution of its volumes in stands of dominant tree species and forest types. The estimation of coarse woody debris stocks was performed based on forest inventory data of Slobozhansky National Nature Park conducted by Ukrainian State Project Forestry Production association “Ukrderzhlisproekt”. Data from 493 forest stands of nine tree species were analyzed. The stock of the following fractions of coarse woody debris was studied: standing dead wood, fallen (downed) dead wood. Data analysis was performed using MS Excel 2016 software. It was found that the total area of forest stands in which standing or downed dead wood was found during forest inventory was 2149.8 ha, or 47.5% of the total forest area of NNP. The total stock of coarse woody debris was 19478 m3, more than 95% of which is concentrated in the stands of Scots pine (Pinus sylvestris L.) (78.8%) and pedunculate oak (Quercus robur L.) (16.6%). Standing dead wood prevailed (62.1%) fallen dead wood (37.9%) in the structure of dead wood volume. The volume of dead wood was in the range of 5–50 m3∙ha–1, and on average in studied forest ecosystems in which it was found was 9.1 m3∙ha–1. In Scots pine forest stands coarse woody debris was found on an area of 1703.5 hectares with total stock of 15355 m3, consists of standing dead trees (9952 m3, 64.8%) and fallen dead wood (5403 m3, 35.2%). The volume of dead wood in forest stands was 5–50 m3∙ha–1, on average – 9.0 m3∙ha–1. In pedunculate oak stands coarse wood debris was found on an area of 384.7 hectares with a total stock of 3224 m3, consists of standing dead wood (1469 m3, 45.6%) and fallen dead wood (1755 m3, 54.4%). The volume of dead wood in forest stands was 5–20 m3∙ha–1, on average – 8.4 m3∙ha–1.


2019 ◽  
Vol 65 (No. 10) ◽  
pp. 408-422
Author(s):  
Vahid Etemad ◽  
Mohsen Javanmiri pour ◽  
Zeinab Foladi

In a natural forest, phases of different dynamics are gradually replaced to create sustainability in the stands. Coarse woody debris is among the most significant structural elements of natural stands that perform an influential position in the identification of dynamic phases. Therefore, the focus of this study is on dead wood conditioning as one of the major structural components in determining the various dynamic phases in the northern forests of Iran as part of the temperate forests. For this study, compartment 326 of Gorazbon District was considered as one of the control parcels of Kheyroud Forest. In this parcel, 25 one-hectare sample plots were selected as permanent plots for a long-term forest structure and succession studies. The coarse woody debris by 100% sampling method was measured. The results showed that there are 8 main phases in this area (gap formation, understorey initiation, stem exclusion, volume accumulation, volume degradation, multiple, lighting, old-growth). The extensive forest area (52%) is located in the understorey initiation and stem exclusion phases. The results also showed that the total average volume of snags and logs was 41.5 m<sup>3</sup>·ha<sup>–1</sup>. Furthermore, the mean dead wood volume in decay classes 1, 2, 3 and 4 was 10.33, 12.22, 9.15 and 83.9 m<sup>3</sup>·ha<sup>–1</sup>, respectively. The average frequency of dead trees in the diameter classes smaller than 25 cm, 25–50 cm and in the diameter class more than 50 cm is 25.79, 6.93, and 4.88. The significance analysis results obtained by ANOVA test showed that there is a significant difference between volume, snag and log stock and the shape of dead wood in various dynamic phases. Therefore, in general, dead wood in the forest differs according to habitat, evolutionary stage (dynamic phases), standing volume and species diversity of the tree species.


2004 ◽  
Vol 155 (2) ◽  
pp. 31-37 ◽  
Author(s):  
Rita Bütler ◽  
Rodolphe Schlaepfer

Dead wood is of paramount importance for forest biodiversity. For this reason it was adopted as an indicator for sustainable forest management by the Ministerial Conference on the protection of forests in Europe. This paper aims to answer the question of how much dead wood is necessary for the maintenance of biodiversity in sub-alpine spruce forest ecosystems. For this purpose we studied the habitat preferences of the three-toed woodpecker, a bird species that depends heavily on dead trees. Previous ecological studies had already demonstrated that this woodpecker is an indicator of spruce forests with a high degree of naturalness and biodiversity. Our field study in Swiss sub-Alpine spruce and Swedish boreal forests showed that, below a threshold level of about 20 m3 standing dead trees per ha, the probability of finding these woodpeckers drastically decreases. Similar results were obtained using a bioenergetic model, which calculated the energy requirements of this insectivorous woodpecker. Based on the results, our recommendation is to ensure a scattering of dead-wood rich areas in forest landscapes. Each area should cover about one square kilometre and have a mean of 5% of standing dead trees (≥ 18 m3 ha–1), and a total of approx. 9% of dead wood(≥ 33 m3 ha–1 standing and fallen).


2015 ◽  
Vol 45 (10) ◽  
pp. 1280-1288 ◽  
Author(s):  
Juha Keränen ◽  
Jussi Peuhkurinen ◽  
Petteri Packalen ◽  
Matti Maltamo

Where airborne laser scanning (ALS) measures the entire aboveground vegetation, the target of a stand-level forest inventory is usually the living tree stock above a given diameter but excluding standing dead trees. The aim here was to investigate the effects of varying field-measured minimum diameters (3–10 cm) and standing dead wood on ALS-based forest inventories. The characteristics considered in this case were volume, basal area, number of stems, mean diameter, and mean height for each species, as well as the total growing stock and the total aboveground biomass. The field data comprised measurements of all trees that were ≥3 cm at breast height (1.3 m) on 601 sample plots located in pine-dominated managed forests in eastern Finland. The results showed that the minimum diameter had a significant effect on the estimates obtained in young forests, for which the three smallest minimum diameter datasets (3, 4, and 5 cm) gave the most accurate estimates. Minimum diameter had no marked influence in the case of middle-aged or mature forests. The inclusion of standing dead trees did not have any effect on the estimates of living tree characteristics. The effect of minimum diameter is minor where large-area inventory applications are concerned; however, especially from a silvicultural point of a view, a minimum diameter of 3 cm should be employed in young forests, for which a large proportion of the tree stock usually consists of small trees, i.e., with diameters of <5 cm.


Author(s):  
А.Ф. Осипов ◽  
И.Н. Кутявин

Приведены результаты исследований структуры и запасов крупных древес- ных остатков (КДО) в среднетаежных сосняках европейского Северо-Востока России, различающихся условиями произрастания и возрастом. К КДО относили сухостойные деревья, валеж и пни диаметром более 6 см. Определены запасы древесины и масса органического вещества в отдельных компонентах (сухостой, валеж, пни) КДО, которые зависят от стадии развития насаждения. Так, в перестойном сосняке черничном наблюдаются более высокие концентрации запасов древесины и органического вещества в гниющей древесине, тогда как в средне- возрастных насаждениях сосняков черничных и чернично-сфагновых более низ- кие. Во всех исследованных насаждениях отмечаются сухостойные деревья. Валеж, пни и сломанные на разной высоте деревья присутствуют в восьми насаждениях. Эти элементы КДО отсутствуют в средневозрастных сосновых древостоях черничного и чернично-сфагнового типа. Выявлено, что в валежнике преобладают деревья, древесина которых находится на начальных стадиях деструкции. По литературным данным представлены результаты исследований запа- сов органического вещества и их распределения по фракциям древостоя. Рассчи- тано соотношение между запасами растущих деревьев и КДО, которое варьирует в широких пределах в зависимости от возраста древостоев. Для оценки взаимо- связи между изучаемыми параметрами были использованы литературные дан- ные, содержащие сведения о массе КДО и древостоя для отдельных пробных площадей. Выявлена положительная (r = 0,57), статистически значимая взаимосвязь между изучаемыми параметрами. Полученные данные можно использовать для уточнения и выведения конверсионных коэффициентов, которые послужат для оценки массы КДО в лесных экосистемах крупных регионов. Structure and stocks of coarse woody debris (CWD) are investigated in the eleven pine forests on European North-East of Russia. Objects under study are differing on forest type and stage of developments. CWD included standing dead trees, fallen dead trees and stumps with a diameter of more than 6 cm. Wood volume and organic matter in separate components of CWD are determined. The mass of CWD depends from stand age. The highest concentrations observed in a overmature pine forest of Myrtillus type but the lowest – in middle-aged stands of Myrtillus and Sphagnosa type. Standing dead trees are noted in all investigated objects. Fallen dead trees and stumps are present in eight stands. These elements are absent in the middle-aged pine stands of Myrtillus and Sphagnosa type. The initial stages of wood destruction dominate in the fallen dead trees. Biomass of stands and it distribution on fractions were present on data that published earlier. The correlation between organic matter mass in CWD and biomass was calculated. It varied in vide range depend on stand age. Literature data were used for estimation relationship between parameters under study. These contained information about forest type, age, CWD mass and stand biomass for separate sample plots. We found positive, statistically significant correlation between CWD stocks and stand biomass. The obtained data can be used to refine and deduce conversion coefficients that will serve to estimate the mass of CWD in forest ecosystems of large regions.


2021 ◽  
pp. 88-97
Author(s):  
O. Chornobrov ◽  
I. Tymochko ◽  
O. Bezrodnova

The article examines the volume of coarse woody detritus in fresh maple-linden-dibrova in Slobozhanskyi National Nature Park. The study was carried out in 115-year-old forest with a predominance of common oak (Quercus robur L.) of natural origin on a sample plot (0.24 ha) by identifying and measuring of standing and lying dead wood components. The volume of dead wood in the forest ecosystem is 32.4 m3·ha–1 and consists of fallen (84.3%) and standing (15.7%). The main part of the dead wood volume is formed by one tree species — common oak (91.3%). In general, woody detritus is characterized by I–IV stages of decomposition, at the same time detritus of III (52.5%) and II (41.7%) stages prevails, detritus of other decomposition stages has insignificant shares (not exceeding 5.0%). No detritus of the last (V) stage of decomposition was detected. The volume of standing dead wood was 5.1 m3·ha–1 and is formed by whole and broken dead trees. In terms of species composition, common oak predominates (80.4%), other species have much smaller shares: small-leaved linden (Tilia cordata Mill.) (13.7%) and Norway maple (Acer platanoides L.) (5.9%). The volume of standing dead wood is dominated by detritus of decomposition stage II (4.8 m3·ha–1, 94.1%), compared with stage I (0.3 m3·ha–1, 5.9%). The volume of lying dead wood is 27.3 m3·ha–1 and is formed by whole fallen trees, fragments of fallen trees (trunks) and thick branches. In terms of species composition dead wood volume is dominated by common oak detritus (25.6 m3·ha–1, 93.7%), and the shares of other species are insignificant. Fallen dead wood is represented by four stages of decomposition (I–IV). In terms of volume, decomposition stage III has an absolute advantage (16.9 m3·ha–1, 61.9%), much less detritus of stage II (8.7 m3·ha–1, 31.9%). Relatively low volume of woody detritus and the absence of dead wood of decomposition stage V may be associated with forestry activities, including selective sanitary cutting and fallen woody debris removal, in the past in modern NNP areas.


2021 ◽  
pp. 102-112
Author(s):  
O. Chornobrov

Dead wood (woody debris) is an important component of forest ecosystems. It performs a number of ecological and environmental functions. The article studies the peculiarities of the formation of coarse wood detritus volume and its qualitative structure in forests in the conditions of fresh sudibrova of the Zmiiini Islands tract of Kaniv Nature Reserve. The study of dead wood was carried out in 140-year-old pine-oak forests of natural origin on a permanent sample plot (0.24 ha) by identifying and measuring of standing and lying deadwood components. It was found that dead wood in the forest ecosystem was formed due to the dying of trees of five species: common oak (Quercus robur L.), Scots pine (Pinus sylvestris L.), Norway maple (Acer platanoides L.), small-leaved lime (Tilia cordata Mill.) and common hornbeam (Carpinus betulus L.), and has a volume 56.3 m3·ha–1. Dead wood volume is dominated by standing dead trees — 82.1%, and the share of lying dead wood, respectively, is 17.9%. The main part of dead wood volume is formed by two tree species — common oak and Scots pine, the share of which together is 94.3%. Common oak and Scots pine is characterized by a predominance of standing dead wood, while for other tree species — lying dead wood. In general, dead wood is formed by detritus of I–IV classes of destruction, at the same time detritus of class II decomposition has a significant advantage (70.5%), recently dead wood has a much smaller share (I class, 24.8%), and other classes of destruction have insignificant shares, which together do not exceed 5.0%. No woody detritus of the last (V) class of destruction was detected. Volume of standing dead wood is 46.2 m3·ha–1, and is formed by whole and broken dead trees. In terms of species composition, common oak has a significant advantage (74.5%), Scots pine has a much smaller share (25.1%), and the share of Norway maple is insignificant (0.4%). The total standing dead wood volume is dominated by wood of class II destruction (33.0 m3·ha–1, 71.4%) compared with class I (13.2 m3·ha–1, 28.6%). Lying dead wood is represented by four classes of destruction (I–IV), however, no woody debris was found at the late (last) stage of decomposition (class V). In terms of volume, the second class of destruction has an absolute advantage (6.7 m3·ha–1, 66.3%), much less class III detritus (2.3 m3·ha–1, 22.8%). Lying dead wood of common oak is represented by all four classes of destruction, among which III (40.5%) and I (33.3%) classes predominate. Lying dead wood of other tree species is characterized by the predominance of II or III classes of destruction. The main factors in the formation of woody detritus in the pine-oak forest in the Zmiiini Islands tract could be the impact of adverse climatic conditions (long periods without precipitation in summer), which led to the weakening of individual trees and their death, gusts of wind that broke individual tree trunks, low-intensity snow breaks, and the influence of biotic factors (insects, pathogens).


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