West Africa - A Safe Haven for Frogs? A Sub-Continental Assessment of the Chytrid Fungus (Batrachochytrium dendrobatidis)

A putative driver of global amphibian decline is the panzootic chytrid fungus Batrachochytrium dendrobatidis (Bd). While Bd has been documented across continental Africa, its distribution in West Africa remains ambiguous. We tested 793 West African amphibians (one caecilian and 61 anuran species) for the presence of Bd. The samples originated from seven West African countries - Bénin, Burkina Faso, Côte d''Ivoire, Ghana, Guinea, Liberia, Sierra Leone - and were collected from a variety of habitats, ranging from lowland rainforests to montane forests, montane grasslands to humid and dry lowland savannahs. The species investigated comprised various life-history strategies, but we focused particularly on aquatic and riparian species. We used diagnostic PCR to screen 656 specimen swabs and histology to analyse 137 specimen toe tips. All samples tested negative for Bd, including a widespread habitat generalist Hoplobatrachus occipitalis which is intensively traded on the West African food market and thus could be a potential dispersal agent for Bd. Continental fine-grained (30 arc seconds) environmental niche models suggest that Bd should have a broad distribution across West Africa that includes most of the regions and habitats that we surveyed. The surprising apparent absence of Bd in West Africa indicates that the Dahomey Gap may have acted as a natural barrier. Herein we highlight the importance of this Bd-free region of the African continent - especially for the long-term conservation of several threatened species depending on fast flowing forest streams (Conraua alleni (“Vulnerable”) and Petropedetes natator (“Near Threatened”)) as well as the “Critically Endangered” viviparous toad endemic to the montane grasslands of Mount Nimba (Nimbaphrynoides occidentalis).     

Vegetation development on pumice at Mount St. Helens, USA

This study explores early vegetation development on pumice at Mount St.Helens. We monitored species annually in a grid of 200 contiguous100-m² plots between 1989 and 1999. Of interestwere how vegetation changed and if it became more homogeneous over time.Speciesrichness and cover increased annually. Diversity(H) stabilized by 1996 and began to decline aslong-livedstress-tolerant species such as Agrostis pallens, Carexmertensii and Penstemon cardwellii began todominate. Protected sites had more species and higher cover than did exposedones. Plots next to relict vegetation had more species and cover than diddistant plots. The vegetation initially was dominated by species with gooddispersal, but subsequently those with poor dispersal became dominant. Wecompared species expansion patterns to a model based on random colonization.Theresults implied that populations with poor dispersal derived from a fewcolonists that then produced seeds for local expansion. Detrendedcorrespondenceanalysis showed a pronounced shift in species composition. This analysis alsoshowed that species composition was becoming more homogeneous over time.However, significant heterogeneity remained and some plots are diverging fromothers. As yet, this vegetation is not developing towards a regional vegetationtype. Rather, an unusual community with Agrostis spp.,Carex spp., Penstemon cardwellii, Lupinuslepidus, Anaphalis margaritacea and Salixcommutata has developed. The accumulation phase of primarysuccessionis nearly complete. The next phase, in which vertical structure develops asSalix and conifers mature, has scarcely begun. It shouldbemarked by the invasion of forest understory species and loss of subalpinemeadowspecies. Assembly rules based on biotic interactions may then become evident.