Density-dependent mortality versus spatial segregation in early life stages of Abies densa and Rhododendron hodgsonii in Central Bhutan
Introduction
Density-dependent processes are important in structuring plant communities. Plants respond to their local neighborhood and effect resources in their close vicinity. Neighborhood processes can influence growth and survival of species positively by facilitation (Callaway et al., 1996, Berkowitz et al., 1995, Kelly et al., 1998) and negatively through competition for resources (Tilman, 1997, Begon et al., 1996), allelopathy (Mallik, 1995), and—indirectly—by specialist herbivores and pathogens (Janzen, 1970, Connell, 1971, Augspurger, 1983, Howe, 1990). Negative neighborhood processes (sensu Stoll and Weiner, 2000) in general and competition in particular lead to more regular spatial patterns over time (Pielou, 1960, Kenkel, 1988, Kenkel, 1988, Duncan, 1991, Moeur, 1997, He and Duncan, 2000).
The presence and intensity of competition depends on the degree of environmental heterogeneity and the response of the plants to this heterogeneity (Lehman and Tilman, 1997, Pacala et al., 1996). Spatial segregation, caused by differential response of plant species to their local environment reduces interspecific competition (Nakashizuka, 2001, Pacala, 1997, Rees et al., 1996). In the early life stages, differential response of plants to different microsites leads to different probabilities of seedling survival, thus qualifying certain sites as regeneration niches (Grubb, 1977) or safe sites (Harper, 1977). Competition and segregation are not mutually exclusive in most ecosystems but interact to varying extents (Brokaw and Busing, 2000). Particularly in plants with large ontogenetic variation in size, e.g. trees, spatial segregation and intra- and interspecific competition may play different roles in different life stages. This is the case with spatial segregation through regeneration niches in early life stages of trees before they increase in size, extend their rooting systems and crowns beyond the spatial extent of the niches and start competing with neighboring trees. Knowing the relative importance of segregation and competition in different life stages helps to understand species coexistence and vegetation dynamics.
Niche partitioning as a mechanism for explaining coexistence was mainly studied in canopy tree species (Szewczyk and Szwagrzyk, 1996, Gray and Spies, 1997, Narukawa and Yamamoto, 2003). Even though the importance of understory species in influencing establishment and early growth and survival of tree species is widely recognized (Coates et al., 1991, Mallik, 1995, Clinton and Vose, 1996, Taylor et al., 1995, Kneeshaw and Bergeron, 1996, Gratzer et al., 1999), few studies characterize mechanisms allowing for coexistence of canopy tree species with long-lived understory species (Manabe and Yamamoto, 1997, Svenning, 2000).
Among these understory species, ericaceous understory plants in general and rhododendron species in particular were shown to compete with, and, in some cases, totally inhibit canopy tree regeneration in temperate forest ecosystems throughout the northern hemisphere (Stainton, 1972, Messier and Kimmins, 1991, Mallik, 1995, Clinton and Vose, 1996, Baker and Van Lear, 1998, Nilsen et al., 1999, Nilsen et al., 2001, Peterken, 2001, Lei et al., 2002). However, most of the evidence stems from forests where anthropogenic influence influenced density and growth of the rhododendron species (in North America: Phillips and Murdy, 1985, Monk et al., 1985, Clinton and Vose, 1996; in the Himalayas: Yoda, 1968, Stainton, 1972, Schmidt-Vogt, 1990, Holzner and Kriechbaum, 1998). Knowledge on the coexistence of rhododendron species and canopy trees in old growth forests with less anthropogenic influence is poor.
R. hodgsonii is an important understory tree species of A. densa forests in the Bhutan Himalayas (Grierson and Long, 1991). Anthropogenic impact on Abies densa forests in the Bhutan Himalayas is low, since commercial use of these forests was limited so far due to restricted access. However, in some areas where logging operations were carried out, severe problems of natural regeneration were reported and attributed to competition with R. hodgsonii (Godi, 1995, Burgi et al., 1992). A better understanding of the mechanisms of coexistence of the two species is a prerequisite of sustainable forest management.
We present the results of a 5-year study on the role of spatial segregation versus density-dependent mortality of regeneration of A. densa and Rhododendron hodgsonii. Our specific objectives were (i) to assess the spatial structure and spatial association of seedlings, saplings and trees, (ii) to test whether mortality in seedlings and saplings were density-dependent or -independent, and (iii) to identify microsite preferences of the two species.
Section snippets
Study area
In the uppermost forest belt in most of Bhutan, pure stands of A. densa (Griff.) (“Eastern Himalayan silver fir”) dominate. These forests extend from 3200 to 3700 m a.s.l. in the high precipitation areas of the front ranges (more than 3000 mm annual precipitation (Eguchi, 1991)), and from 3600 to 4100 m in the somewhat drier interior (annual rainfall of about 1200 mm). A. densa forests cover 3500 km2 or 8.6% of the area of Bhutan.
The current study was carried out in two watersheds (totaling 5700 ha)
Methods
Density-dependent processes can be detected by characterizing the temporal development of spatial patterns and interspecific associations. This was frequently applied in communities with a fast turnover like grasslands (Suzuki et al., 2003, Law et al., 1997, Herben et al., 2000). In forests, density-dependent processes were frequently studied by comparing patterns of live plus remaining dead individuals with spatial patterns of live individuals (Kenkel, 1988, Kenkel, 1988, Duncan, 1991, He and
Age structure and survival of seedlings and saplings
The age class distribution of seedlings and saplings shows that during the last 20 years recruitment was continuous for both species (Fig. 1). In all but one plot, R. hodgsonii had higher densities in younger age classes. On 10 plots, A. densa seedlings and saplings (height ≤200 cm) of more than 20 years were found while only one plot had R. hodgsonii of more than 20 years in the same height class. Maximum age of A. densa and R. hodgsonii saplings was 39 and 21 years, respectively. Ten out of 12
Patterns of spatial segregation
The interspecific spatial correlation (Rδ) of individuals of A. densa and R. hodgsonii in the same size class was increasingly negative with increasing size class. This was also true for the changes in Rδ from 1996 to 2001. Individuals of more than 100 cm height showed an increasingly strong negative spatial correlation indicating that in these size classes interspecific competition is getting stronger while it is absent up to 25 cm height and only weakly evident from 25 cm up to 100 cm.
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