Snag Densities in Old-Growth and Second-Growth Appalachian Forests

1983 ◽  
Vol 47 (2) ◽  
pp. 376 ◽  
Author(s):  
William C. McComb ◽  
Robert N. Muller
Keyword(s):  
Old Growth ◽  
Second Growth ◽  
Appalachian Forests

Macrofungi from six habitats over five years in Clayoquot Sound, Vancouver Island

2004 ◽  
Vol 82 (10) ◽  
pp. 1518-1538 ◽  
Author(s):  
Christine Roberts ◽  
Oluna Ceska ◽  
Paul Kroeger ◽  
Bryce Kendrick
Keyword(s):  
British Columbia ◽  
Rare Species ◽  
Vancouver Island ◽  
The Other ◽  
Forest Types ◽  
Natural Ecosystems ◽  
Old Growth ◽  
Second Growth ◽  
Clayoquot Sound

Over 5 years, macrofungi from six habitats in Clayoquot Sound, Vancouver Island, British Columbia, were documented. Habitats were categorized as dune, spruce fringe, old-growth rainforest, second-growth forest, bog, or estuarine. All but the second-growth forest are natural ecosystems. A total of 551 taxa of macrofungi were recorded. Between 17% and 36% of the species in any one habitat were found only in that habitat. The most frequently encountered and ubiquitous species was Craterellus tubaeformis (Fr.) Quel., found in all years, habitats, and sites. Of the 551 taxa, only 28 were found every year, and 308 were found in only 1 year. Rare species that were recorded include Cordyceps ravenelii Berkeley & Curtis, Hygrophorus inocybiformis Smith, and Tricholoma apium Schaeffer in the dunes and Stereopsis humphreyi (Burt) Redhead in the spruce fringe. Similarities between habitats based on taxa in common showed that bog and estuarine habitats had only 9%–17% in common with each other and the other habitats, whereas dune, spruce fringe, and the two forest types shared 21%–31% of their species. Old-growth rainforest yielded approximately 4 times as many species as bog and estuarine habitats, and approximately 1.5 times as many as the other three habitats.Key words: Clayoquot Sound, Vancouver Island, macrofungi, habitats, biodiversity.

Forest Regrowth on the Cumberland Plateau and Implications for Productive Management

1983 ◽  
Vol 7 (4) ◽  
pp. 208-212 ◽  
Author(s):  
Robert N. Muller
Keyword(s):  
Species Composition ◽  
Basal Area ◽  
Stand Density ◽  
Cumberland Plateau ◽  
Old Growth ◽  
Nutrient Pools ◽  
Old Growth Forest ◽  
Composition And Structure ◽  
Second Growth ◽  
Commercial Species

Abstract An old-growth forest and a 35-year-old, second-growth forest on the Cumberland Plateau were studied to compare species composition and structure. Species composition and total basal area of the two stands did not differ, although total stand density was 19 percent lower and basal area of commercial species was 25 percent higher in the old-growth than in the second-growth stand. Analysis of size-class distributions showed that both stands were best represented by an inverse J-shaped distribution, which best describes old-age stands. The rapid regeneration of the second-growth stand seems to be the result of minimal disturbance to accumulated nutrient pools in the soil. The importance of these accumulated nutrient pools and implications for forest management on the Cumberland Plateau are discussed.

Species Diversity and Composition in Old Growth and Second Growth Rich Coves of The Southern Appalachian Mountains

Castanea ◽  
2009 ◽  
Vol 74 (1) ◽  
pp. 27-38 ◽  
Author(s):  
B. Clay Jackson ◽  
J. Dan Pittillo ◽  
H. Lee Allen ◽  
Thomas R. Wentworth ◽  
Bronson P. Bullock ◽  
...  
Keyword(s):  
Species Diversity ◽  
Appalachian Mountains ◽  
Old Growth ◽  
Southern Appalachian Mountains ◽  
Southern Appalachian ◽  
Second Growth

scholarly journals Abundance and Size Distribution of Cavity Trees in Second-Growth and Old-Growth Central Hardwood Forests

2005 ◽  
Vol 22 (3) ◽  
pp. 162-169 ◽  
Author(s):  
Zhaofei Fan ◽  
Stephen R. Shifley ◽  
Martin A. Spetich ◽  
Frank R. Thompson ◽  
David R. Larsen
Keyword(s):  
Hardwood Forests ◽  
Size Class ◽  
Cumulative Probability ◽  
Age Classes ◽  
Old Growth ◽  
Plot Size ◽  
Class A ◽  
Second Growth ◽  
Tree Estimation ◽  
Cavity Tree

Abstract In central hardwood forests, mean cavity-tree abundance increases with increasing stand-size class (seedling/sapling, pole, sawtimber, old-growth). However, within a size class, the number of cavity trees is highly variable among 0.1-ha inventory plots. Plots in young stands are most likely to have no cavity trees, but some plots may have more than 50 cavity trees/ha. Plots in old-growth stands often had 25 to 55 cavity trees/ha, but individual plots ranged from 0 to 155/ha. The Weibull probability density function was used to mathematically describe the variation in cavity-tree abundance for plots in stands of differing size (or age) class. A graph of the cumulative probability of cavity-tree abundance is a particularly easy way for managers to estimate the probability that a stand of a given size class will have any specified number of cavity trees per hectare. Results for individual plots or stands can be combined to estimate cavity abundance probabilities for landscapes. Because the results are presented in terms of plot-size classes (or age classes), this approach to cavity tree estimation is compatible with relatively simple forest inventorysystems.North. J. Appl. For. 22(3):162–169.

Testing for stand dynamics effects on red spruce growth trends

1987 ◽  
Vol 17 (12) ◽  
pp. 1487-1495 ◽  
Author(s):  
Paul C. Van Deusen
Keyword(s):  
New York ◽  
Red Spruce ◽  
Stand Dynamics ◽  
Growth Data ◽  
Growth Reduction ◽  
Old Growth ◽  
Usda Forest Service ◽  
Increment Core ◽  
Second Growth ◽  
Insect Activity

Increment-core data for old-growth red spruce (Picearubens Sarg.) were collected for dendrochonological purposes and compared with second-growth data obtained from USDA Forest Service inventory plots in Maine, New Hampshire, Vermont, and New York. The research objective was to test the hypothesis suggested by J. W. Hornbeck and R. B. Smith (1985, Can. J. For. Res. 15: 1199–1201) that red spruce show reduced growth in the Northeastern United States due to stand dynamics resulting from past logging and insect activity. A graphical approach and a modeling approach based on the Kalman filter were employed. The results indicate that the growth reduction is greater in second-growth stands and that the second-growth stands are converging to an old-growth condition. This supports the stand dynamics hypothesis for second-growth stands.

Distribution of cavity trees in midwestern old-growth and second-growth forests

2003 ◽  
Vol 33 (8) ◽  
pp. 1481-1494 ◽  
Author(s):  
Zhaofei Fan ◽  
Stephen R Shifley ◽  
Martin A Spetich ◽  
Frank R Thompson III ◽  
David R Larsen
Keyword(s):  
Regression Tree ◽  
Logistic Models ◽  
Species Group ◽  
Classification And Regression Tree ◽  
Old Growth ◽  
Threshold Size ◽  
Decay Class ◽  
Second Growth ◽  
Classification And Regression ◽  
Cavity Tree

We used classification and regression tree analysis to determine the primary variables associated with the occurrence of cavity trees and the hierarchical structure among those variables. We applied that information to develop logistic models predicting cavity tree probability as a function of diameter, species group, and decay class. Inventories of cavity abundance in old-growth hardwood forests in Missouri, Illinois, and Indiana found that 8–11% of snags had at least one visible cavity (as visually detected from the ground; smallest opening [Formula: see text]2 cm diameter), about twice the percentage for live trees. Five percent of live trees and snags had cavities on mature ([Formula: see text]110 years) second-growth plots on timberland in Missouri. Because snags accounted for typically no more than 10% of standing trees on any of these sites, 80–85% of cavity trees are living trees. Within the subset of mature and old-growth forests, the presence of cavities was strongly related to tree diameter. Classification and regression tree models indicated that 30 cm diameter at breast height (DBH) was a threshold size useful in distinguishing cavity trees from noncavity trees in the old-growth sample. There were two diameter thresholds in the mature second-growth sample: 18 and 44 cm DBH. Cavity tree probability differed by species group and increased with increasing decay class.

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