Long-term effects of logging on African primate communities: a 28-year comparison from Kibale National Park, Uganda

被引:187
作者
Chapman, CA [1 ]
Balcomb, SR
Gillespie, TR
Skorupa, JP
Struhsaker, TT
机构
[1] Univ Florida, Dept Zool, Gainesville, FL 32611 USA
[2] Wildlife Conservat Soc, Bronx, NY 10460 USA
[3] US Fish & Wildlife Serv, Div Environm Contaminants, Sacramento, CA 95821 USA
[4] Duke Univ, Dept Biol Anthropol & Anat, Durham, NC 27708 USA
关键词
D O I
10.1046/j.1523-1739.2000.98592.x
中图分类号
X176 [生物多样性保护];
学科分类号
090705 ;
摘要
If logging is to be compatible with primate conservation, primate populations must be expected to recover from the disturbance and eventually return to their former densities. Surveys conducted over 28 years were used to quantify the long-term effects of both low- and high-intensity selective logging on the density of the five common primates in Kibale National Park, Uganda. The most dramatic exception to the expectation that primate populations will recover following logging was that group densities of Cercopithecus mitis and C. ascanius in the heavily logged area continued to decline decades after logging. Procolobus tephrosceles populations were recovering in the heavily logged areas, but the rate of increase appeared to be slow (0.005 groups/km(2) per year). Colobus guereza appeared to do well in some disturbed habitats and were found at higher group densities in the logged areas than in the unlogged area. There was no evidence of an increase in Lophocebus albigena group density in the heavily logged area since the time of the logging, and there was a tendency for its population to be lower in heavily logged areas that in lightly logged areas. In contrast to the findings from the heavily logged area, none of the species were found at a lower group density in the lightly logged area than in the unlogged area, and group densities in this area were not changing at a statistically significant rate. The results of our study suggest that, in this region, low-intensity selective logging could be one component of conservation plans for primates; high-intensity logging, however, which is typical of most logging operations throughout Africa, is incompatible with primate conservation.
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页码:207 / 217
页数:11
相关论文
共 68 条
[1]  
ALTMANN J, 1977, Primates, V18, P315, DOI 10.1007/BF02383111
[2]  
[Anonymous], THESIS MICHIGAN STAT
[3]  
Bennett Elizabeth L., 1995, P66
[4]   THE BIOLOGICAL DYNAMICS OF TROPICAL RAIN-FOREST FRAGMENTS [J].
BIERREGAARD, RO ;
LOVEJOY, TE ;
KAPOS, V ;
DOSSANTOS, AA ;
HUTCHINGS, RW .
BIOSCIENCE, 1992, 42 (11) :859-866
[5]   TROPICAL SECONDARY FORESTS [J].
BROWN, S ;
LUGO, AE .
JOURNAL OF TROPICAL ECOLOGY, 1990, 6 :1-32
[6]  
Buckland S. T., 1993, Distance sampling: estimating abundance of biological populations.
[7]  
BURNHAM KP, 1980, WILDLIFE MONOGRAPHS, V72
[8]   COMPARATIVE ECOLOGY OF BLUE MONKEYS (CERCOPITHECUS-MITIS) IN HIGH-DENSITY AND LOW-DENSITY SUBPOPULATIONS [J].
BUTYNSKI, TM .
ECOLOGICAL MONOGRAPHS, 1990, 60 (01) :1-26
[9]  
Chapman C., 1988, BRENESIA, V30, P67
[10]   Spatial and temporal variability in the structure of a tropical forest [J].
Chapman, CA ;
Chapman, LJ ;
Wrangham, R ;
Isabirye-Basuta, G ;
Ben-David, K .
AFRICAN JOURNAL OF ECOLOGY, 1997, 35 (04) :287-302