scholarly journals Thinning Intensity for Large Diameter Trees in Korean White Pine Plantation of South Korea

2017 ◽  
Vol 33 (1) ◽  
pp. 74-77
Author(s):  
Daesung Lee ◽  
Yeongwan Seo ◽  
Jiyoung Park ◽  
Jungkee Choi
2002 ◽  
Vol 78 (4) ◽  
pp. 539-549 ◽  
Author(s):  
Paul D Anderson ◽  
John C Zasada ◽  
Glen W Erickson ◽  
Zigmond A Zasada

A white pine (Pinus strobus L.) stand at the western margin of the species range, approximately 125 years of age at present, was thinned in 1953 from 33.5 m2 ha-1 to target residual basal areas of 18.4, 23.0, 27.5, and 32.1 m2 ha-1 . Repeated measurement over the following 43-years indicated that the greatest total volume production and the greatest number of large diameter trees occurred in the unit of highest residual density. Over time, the distribution of stems was predominantly random although mortality between 1979 and 1996 resulted in a tendency for clumping in the 23.0 and 27.5 m2 ha-1 treatments. DNA analysis indicated that thinning intensity had little effect on the genetic diversity of residual white pine. This study suggests that mature white pine stands in northern Minnesota may be managed at relatively high densities without loss of productivity. However, regardless of overstory density, there was little or no white pine regeneration occurring in this stand. Key words: thinning, growth, genetic diversity, molecular markers, spatial pattern, regeneration


1959 ◽  
Vol 40 (6) ◽  
pp. 305-309 ◽  
Author(s):  
Merle G. Lloyd ◽  
Clyde A. O'Dell ◽  
H. J. Wells

Silver-iodide particles were used to simulate the movement of white-pine blister-rust spores on a white-pine plantation in northern Idaho where long-distance spread of the disease is suspected. It was hypothesized that cold drainage winds were carrying spores down to a relatively warm lake where convective currents carried the spores aloft. The spores were then distributed over the plantation when a favorable upper-air flow prevailed. Silver-iodide particles were released at the suspected source of infection and traced into the plantation.


2004 ◽  
Vol 164 (3) ◽  
pp. 527-541 ◽  
Author(s):  
Dai Hirose ◽  
Junichi Kikuchi ◽  
Natsumi Kanzaki ◽  
Kazuyoshi Futai
Keyword(s):  

2016 ◽  
Author(s):  
Glendon W. Smalley ◽  
Scott J. Torreano ◽  
B. Hayes Swinney ◽  
Michael R. Fulkerson ◽  
Ryan W. Barry ◽  
...  

2003 ◽  
Vol 79 (3) ◽  
pp. 632-644 ◽  
Author(s):  
Bruce J Stewart ◽  
Peter D Neily ◽  
Eugene J Quigley ◽  
Lawrence K Benjamin

A study of four old-growth stands in Nova Scotia was conducted to document the ecological characteristics of these currently rare Acadian forest ecosystems. Stands were selected to represent the two dominant climax forest types, hemlock–red spruce–eastern white pine, and sugar maple–yellow birch–beech. Data include measurements of age structure, species composition, diameter distribution, basal area, height, coarse woody debris, snags, vertical structure, and canopy condition. All stands were determined to be uneven-aged. Old-growth reference ages calculated for the stands ranged from 164 to 214 years. All stands displayed broad diameter distributions that had peak basal area representation in the 40- to 50-cm diameter classes. Volumes of dead wood ranged from 111 to 148 m3/ha in the softwood stands and from 63 to 83m3/ha in the hardwood stands. Dead wood consisted of approximately one-third snags and two thirds downed coarse woody debris. Measurements from the stands were used to evaluate Nova Scotia's recently developed Old Forest Scoring System. Six stand attributes were rated for a maximum score of 100: stand age, primal value, number of large-diameter trees, length of large-diameter dead wood, canopy structure, and understorey structure. Based on the age attribute, three of the four stands were classed as Mature Old Growth and one was very close, indicating that all are in the shifting mosaic stage of late forest succession. The scores for all stands were relatively high, ranging from 75 to 85, as would be expected from some of the best old-growth stands in the province. Key words: old growth, climax, primal, late succession, uneven-aged, scoring, coarse woody debris, age structure, diameter, Acadian forest, northern hardwood, red spruce, eastern hemlock, white pine, sugar maple, yellow birch, American beech


2001 ◽  
Vol 77 (4) ◽  
pp. 721-734 ◽  
Author(s):  
William C. Parker ◽  
Daniel C. Dey ◽  
Steven G. Newmaster ◽  
Ken A. Elliott ◽  
Eric Boysen

The effects of thinning on growth and survival of white pine (Pinus strobus L.), white ash (Fraxinus americana L.), and red oak (Quercus rubra L.), and understory plant diversity were examined in a young red pine (Pinus resinosa Ait.) plantation. Five years after thinning, seedling diameter, height, and stem volume were positively correlated with thinning intensity and the size of canopy openings. Percent survival did not differ among thinning treatments, but was significantly higher in white ash and white pine than red oak. Understory vegetation included 113 species, with species richness increasing with thinning intensity and proximity to neighbouring plant communities. Thinning to create relatively large canopy openings in combination with underplanting can promote the natural succession of young pine plantations to native forest species. Keywords: direct seeding, plant diversity, natural regeneration, red oak, restoration, white ash, white pine


1990 ◽  
Vol 20 (6) ◽  
pp. 857-860 ◽  
Author(s):  
James M. Vose ◽  
Wayne T. Swank

We used a direct approach to quantify foliar N absorption by exposing foliage of mature eastern white pine (Pinusstrobus L.) to 15N-labeled nitric acid vapor (HNO3). Foliage on terminal portions of branches in a 31-year-old white pine plantation was enclosed in 9.0-L teflon film branch cuvettes and exposed to 10, 50, and 100 ppb H15NO3 for 12–30 h. Foliar absorption rates ranged from 0.026 μg 15N•g−1•h−1 at 10 ppb to 0.267 μg 15N•g−1•h−1 at 100 ppb. Extrapolation to the entire canopy resulted in an estimated absorption of 0.30–0.50 kg N•ha−1•year−1 at ambient HNO3 concentrations. In contrast, canopy input–output estimates for the same forest stand indicated a depletion of 2.3 kg•N•ha−1•year−1 by the forest canopy.


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