Mountains provide an interesting context in which to study the many facets of biodiversity in response to macroclimate, since environmental conditions change rapidly due to elevation. Although the decrease in biodiversity with increasing elevation is generally accepted, our understanding of the variation of functional diversity along altitudinal gradients is still poorly known. The partitioning of diversity into spatial components can help to understand the processes that influence the distribution of species, and these studies are urgently needed in face of the increasing threats to mountain environments throughout the world. We describe the distribution of dung beetle diversity along an altitudinal gradient on a tropical mountain in southeastern Brazil, including the spatial partitioning of taxonomic and functional diversities. The altitudinal gradient ranged from 800 up to 1400 m a.s.l. and we collected dung beetles at every 100 m of altitude. We used the Rao Index to calculate γ, α and β diversity for taxonomic and functional diversity of dung beetles. Climatic, soil and vegetation variables were used to explain variation in community attributes along the altitudinal gradient. Dung beetle richness declined with altitude and was related to climatic and vegetation variables, but functional diversity did not follow the same pattern. Over 50% of γ taxonomic diversity was caused by among altitudes diversity (β), while almost 100% of functional diversity was due to the α component. Contrasting β taxonomic with β functional diversity, we suggest that there is ecological redundancy among communities and that the environment is filtering species in terms of the Grinnellian niche, rather than the Eltonian niche. β taxonomic diversity is caused mainly by the turnover component, reinforcing the hypothesis of environmental filtering. Global warming may have strong effects on mountain communities due to upslope range shifts and extinctions, and these events will lead to an even larger than previously expected loss of diversity as dung beetles γ taxonomic diversity is caused mainly by the β component.

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SUMMARYControl of the midgut pH in Lutzomyia longipalpis enables the insect's digestive system to deal with different types of diet. Phlebotomines must be able to suddenly change from a condition adequate to process a sugar diet to one required to digest blood. Prior to blood ingestion, the pH in the midgut is maintained at ~6 via an efficient mechanism. In the abdominal midgut, alkalization to a pH of ~8 occurs as a consequence of the loss of CO 2 from blood (CO 2 volatilization) and by a second mechanism that is not yet characterized. The present study aimed to characterize the primary stimuli, present in the blood, that are responsible for shutting down the mechanism that maintains a pH of 6 and switching on that responsible for alkalization. Our results show that any ingested protein could induce alkalization. Free amino acids, at the concentrations found in blood, were ineffective at inducing alkalization, although higher concentrations of amino acids were able to induce alkalization. Aqueous extracts of midgut tissue containing putative hormones from intestinal endocrine cells slightly alkalized the midgut lumen when applied to dissected intestines, as did hemolymph collected from blood-fed females. Serotonin, a hormone that is possibly released in the hemolymph after hematophagy commences, was ineffective at promoting alkalization. The carbonic anhydrase (CA) enzyme seems to be involved in alkalizing the midgut, as co-ingestion of acetazolamide (a CA inhibitor) with proteins impaired alkalization efficiency. A general model of alkalization control is presented.

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Patterns of termite richness along elevation gradients may be related to different responses by termite functional groups to changes in environmental conditions. We investigated the distribution of termite species richness along an elevational gradient of cerrado and rupestrian grasslands in the Espinhaço Mountain Range, in Brazil. Fifty termite species were recorded, with the family Termitidae being dominant; 16 species are endemic to open areas of cerrado and 1 species, Cortaritermes rizzinii, is endemic and restricted to mountaintop grassland habitats. Termite richness declined with increasing elevation, with the main factors associated with the reduction being climactic (air temperature, air and soil humidity, and radiation) and vegetation variables. Different termite communities were found along the elevational gradient, which were also strongly influenced by changes in climate and vegetation. On the other hand, the same functional groups were present at the different elevations, although represented by different species.