Ecological Studies in Four Contrasting Lowland Rain Forests in Gunung Mulu National Park, Sarawak: II. Litterfall, Litter Standing Crop and Preliminary Observations on Herbivory

1983 ◽  
Vol 71 (1) ◽  
pp. 261 ◽  
Author(s):  
John Proctor ◽  
J. M. Anderson ◽  
S. C. L. Fogden ◽  
H. W. Vallack
Oryx ◽  
1986 ◽  
Vol 20 (2) ◽  
pp. 89-94 ◽  
Author(s):  
Jesse C. Hillman

Ethiopia does not often receive publicity for its wildlife conservation work, but there have been a commendable number of achievements over the last 15 years or so. For the last two years the author has been carrying out ecological studies to formulate management plans in the Bale Mountains area, which is in the process of being established as a national park. As a result of the developments and protection already afforded, numbers of the endemic mountain nyala have increased considerably.


Koedoe ◽  
1982 ◽  
Vol 25 (1) ◽  
Author(s):  
I. L Rautenbach ◽  
I. W Espie

The Kruger National Park (KNP), Republic of South Africa, is one of the most intensively studied areas of Africa. Underlying the management practices for such a Park as well as broad-based ecological studies, is a thorough knowledge of the diversity and distribution of the fauna and flora under conservation.


2009 ◽  
Vol 25 (6) ◽  
pp. 665-669 ◽  
Author(s):  
Scott A. Parsons ◽  
Luke P. Shoo ◽  
Stephen E. Williams

Litter standing crop (LSC) is the quantity of plant detritus on the floor in forested environments. Knowledge of LSC is important in understanding many ecological phenomena. These include studies of litterfall, decomposition/litter turnover rates and nutrient cycling (Anderson et al. 1983, Dent et al. 2006), general plant performance (Benítez-Malvido & Kossmann-Ferraz 1999), other ecosystem processes such as the effects of fire (Odiwe & Muoghalu 2003) and fauna (Frith & Frith 1990, Giaretta et al. 1999, Levings & Windsor 1985). The determination of accurate annual average LSC data, may require monitoring over long periods due to seasonality and sometimes sporadic nature of litterfall and decomposition rates (Clark et al. 2001). Furthermore, the effects of topography and water movement create the need for both representative site selection and sufficient spatial coverage.


Oryx ◽  
1996 ◽  
Vol 30 (3) ◽  
pp. 207-217 ◽  
Author(s):  
Timothy G. O'Brien ◽  
Margaret F. Kinnaird

Bukit Barisan Selatan National Park in south-west Sumatra is one of the largest protected areas in Sumatra and thus of considerable importance to the conservation of biodiversity in Indonesia. Until recently, little was known of the wildlife in the park. The authors' surveys document the presence of an intact community of the birds and mammals known to occur in lowland Sumatran rain forests. While hunting and collection of forest products threaten a number of plant and animal species in the park, the primary threat to the park's integrity is from agricultural encroachment and expansion of enclaves beyond their boundaries. The future survival of Bukit Barisan National Park and its wildlife requires that active measures be taken to curb non-sustainable exploitation of plants and wildlife. It will also be necessary to resolve land-use conflicts with communities in, and adjacent to, the park.


2000 ◽  
Vol 77 (12) ◽  
pp. 1699-1711 ◽  
Author(s):  
Thomas E O'Dell ◽  
Joseph F Ammirati ◽  
Edward G Schreiner

Sporocarps of epigeous ectomycorrhizal fungi and vegetation data were collected from eight Tsuga heterophylla (Raf.) Sarg. - Pseudotsuga menziesii (Mirb.) Franco stands along a wet to dry gradient in Olympic National Park, Washington, U.S.A. One hundred and fifty species of ectomycorrhizal fungi were collected from a total sample area of 2.08 ha. Over 2 years, fungal species richness ranged from 19 to 67 taxa per stand. Sporocarp standing crop ranged from 0 to 3.8 kg/ha, averaging 0.58 kg/ha, 0.06 kg/ha in spring and 0.97 kg/ha in fall. Sporocarp standing crop and fungal species richness were correlated with precipitation. These results demonstrated that ectomycorrhizal fungal sporocarp abundance and species richness can be partly explained in terms of an environmental gradient.


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