The contribution of cacao agroforests to the conservation of lower canopy ant and beetle diversity in Indonesia

The ongoing destruction of tropical rainforests has increased the interest in the potential value of tropical agroforests for the conservation of biodiversity. Traditional, shaded agroforests may support high levels of biodiversity, for some groups even approaching that of undisturbed tropical forests. However, it is unclear to what extent forest fauna is represented in this diversity and how management affects forest fauna in agroforests. We studied lower canopy ant and beetle fauna in cacao agroforests and forests in Central Sulawesi, Indonesia, a region dominated by cacao agroforestry. We compared ant and beetle species richness and composition in forests and cacao agroforests and studied the impact of two aspects of management intensification (the decrease in shade tree diversity and in shade canopy cover) on ant and beetle diversity. The agroforests had three types of shade that represented a decrease in tree diversity (high, intermediate and low diversity). Species richness of ants and beetles in the canopies of the cacao trees was similar to that found in lower canopy forest trees. However, the composition of ant and beetle communities differed greatly between the agroforest and forest sites. Forest beetles suffered profoundly from the conversion to agroforests: only 12.5% of the beetle species recorded in the forest sites were also found in the agroforests and those species made up only 5% of all beetles collected from cacao. In contrast, forest ants were well represented in agroforests, with 75% of all species encountered in the forest sites also occurring on cacao. The reduction of shade tree diversity had no negative effect on ants and beetles on cacao trees. Beetle abundances and non-forest ant species richness even increased with decreasing shade tree diversity. Thinning of the shade canopy was related to a decrease in richness of forest ant species on cacao trees but not of beetles. The contrasting responses of ants and beetles to shade tree management emphasize that conservation plans that focus on one taxonomic group may not work for others. Overall ant and beetle diversity can remain high in shaded agroforests but the conservation of forest ants and beetles in particular depends primarily on the protection of natural forests, which for forest ants can be complemented by the conservation of adjacent shaded cacao agroforests.     

The spatial distribution of beetles within the canopies of oak trees in Richmond Park, U.K.

1. 5054 adult beetles of 144 species were collected in a total of 696 1‐m² collecting trays by knockdown insecticide fogging of 36 different oak trees in closed canopy woodland at Richmond Park, U.K., with three of the trees sampled on each of 12 dates, at 2‐ to 3‐week intervals, between April and October 1984. 2. In late spring (April/May), more individuals and species of beetles were collected in trays close to the trunks of trees than in trays more distant from the trunk. The reverse was the case in late September/October. Neither pattern prevailed in the intervening months. 3. Individual species exhibited a variety of patterns, with some species more abundant near the trunk, e.g. Leiopus nebulosus (L.), Strophosoma melanogrammum (Forster), Cylindronotus laevioctostriatus (Goeze), and Dromius agilis (Fabricius), and some less abundant near the trunk, e.g. Curculio pyrrhoceras (Marsham) and Rhynchaenus signifer (Creutzer). For Adalia decempunctata (L.), this preference changed with season. The observed species preferences for parts of a tree crown near or distant from the main trunk are discussed with reference to their known biologies. 4. No pronounced pattern of preference for north‐ or south‐facing aspects of trees in closed canopy woodland was observed, however populations of some species exhibited patterns of within‐tree distribution that correlate with compass angle; for one species, the ladybird Adalia decempunctata, this distribution changed with season and between colour morphs.     

Species number, species abundance and body length relationships of arboreal beetles in Bornean lowland rain forest trees

ABSTRACT.

• 1 The relationships between number of species, abundance per species, and body length are examined for 859 species of beetles in samples of arthropods collected from ten Bornean lowland forest trees by insecticide fogging. Similar relationships are examined for different feeding guilds of these beetles, and for those beetles from different species of trees.
• 2 The data are used to construct four interrelated graphs, namely species: abundance, species: body length, population abundance: body length and total number of individuals: body length distributions.
• 3 In contrast to a number of previous studies, no consistent linear relationship between population density and body length was found for the Bornean beetles and it is suggested that, as in birds, the added dispersal ability of flight reduces critical population densities necessary for persistence in small species. Previous relationships between body weight and population abundance may also be artefacts of the way in which data were gathered.
• 4 Despite large samples, we failed to locate the mode in plots of the number of species in each abundance category (species: abundance distribution).
• 5 Species: body length and total number of individuals: body length plots were similar to those found in previous studies, although using data for Coleoptera alone may have produced a steeper decline in the total number of individuals as body size increases than is apparent in samples of all arthropods.
• 6 We present the first three-dimensional graph relating numbers of species, body lengths and population abundances. The surface of this three-dimensional relationship is relatively simple.

     

The arboreal ants of a Neotropical rain forest show high species density and comprise one third of the ant fauna

In tropical rain forests, the ant community can be divided into ground and arboreal faunas. Here, we report a thorough sampling of the arboreal ant fauna of La Selva Biological Station, a Neotropical rain forest site. Forty-five canopy fogging samples were centered around large trees. Individual samples harbored an average of 35 ant species, with up to 55 species in a single sample. The fogging samples yielded 163 observed species total, out of a statistically estimated 199 species. We found no relationship between within-sample ant richness and focal tree species, nor were the ant faunas of nearby trees more similar to each other than the faunas of widely spaced trees. Species density was high, and beta diversity was low: A single column of vegetation typically harbors at least a fifth of the entire arboreal ant fauna. Considering the entire fauna, based on 23,326 species occurrence records using a wide variety of collecting methods, 182 of 539 observed species (196 of 605, estimated statistically) were entirely arboreal. The arboreal ant fauna is thus about a third of the total La Selva ant fauna, a robust result because inventory completeness was similar for ground and arboreal ants. The taxonomic history of discovery of the species that make up the La Selva fauna reveals no disproportionately large pool of undiscovered ant species in the canopy. The "last biotic frontier" for tropical ants has been the rotten wood, leaf litter, and soil of the forest floor.     

西双版纳高峭蛛新属新种描述(蜘蛛目,蟹蛛科)

描述了采自云南西双版纳热带雨林的蟹蛛1新属高峭蛛属及1新种胶高峭蛛Acrotmarus gummosus gen.et sp.nov..新种模式标本保存在中国科学院动物研究所.高峭蛛属,新属Acrotmarus gen.nov.与蟹蛛科蟹蛛亚科峭腹蛛族中的其它属的主要区别在于:后侧眼眼丘大而隆起,雄蛛触肢插入器呈薄片状,基部有宽缘,其端部具1凹陷,末端呈钩状.本属近似于非洲的Pherecydes O.P.-Cambridge,1883,但有以下不同:前者仅后侧眼在隆起的眼丘上,后者的前侧眼、后侧眼均在隆起的眼丘上;前者雌蛛的后侧眼间距/头胸部宽为0.93,后者为1.29;前者雌蛛前中眼间距/前中、侧眼间距为0.97,后者为1.52.本属的生殖器官结构与Pherecydes差异明显:前者雄蛛触肢有VTA而后者缺乏,前者插入器扁平片状而后者丝状;前者外雌器有兜而后者无.词源:新属属名由于标本系从高层雨林冠层采集而来,且与峭腹蛛族的属在外形上有相似性.胶高峭蛛,新种Acrotmarus gummosus sp.nov.(图1～3,6～21)正模♂.副模:24 ♂ ♂,15♀ ♀,云南省西双版纳国家自然保护区勐仑保护区的热带雨林及橡胶林,2007年7～8月间,郑国采;1 ♂,西双版纳勐仑镇绿石林森林公园,2009年11月15日,唐果、姚志远采.词源:新种种名源自新种部分标本采于橡胶林冠层.     

Arthropods within the woody element of hedgerows and their distribution pattern

1 The diversity and abundance of arthropods within hedgerows was investigated using insecticide fogging. In total, 13 390 arthropods were collected from 181 m³ of hedge (2% of the total volume). The taxonomic diversity of the total sample included 51 families in 13 orders, all within the phylum Arthropoda. Five orders accounted for 90% of all arthropods: Araneae, Coleoptera, Diptera, Hemiptera and Hymenoptera. The predators were the dominant functional group accounting for 40% of the total sample. 2 The linear distribution of hedgerow arthropod assemblages was investigated by sampling arthropods in 13 hedges at seven equidistant points along each hedge. Abundance of most arthropod taxa and the four functional groups (predators, parasitoids, herbivores and scavengers) consistently showed a clumped distribution along hedges, with high numbers at both ends and in the middle section. Hedge ends were defined either as a node, where the hedge intersected with another hedge, or as a gateway prior to an adjacent landscape feature such as a wood. Aggregation of arthropods at the nodes may reflect preferable microclimatic conditions at hedgerow junctions, whereas aggregation at a gap suggests the gap acted as a barrier to movement. The aggregation at the centre remains unexplained but may be a manifestation of the movement of individual arthropods along the hedgerow. 3 The great abundance and diversity of arthropods found in the present study emphasizes the status of hedges as one of the most important noncrop habitats on farmland. The arthropods that they contain may act as food for other farmland species, aid pest control and contribute to crop pollination.     

The Importance of Primary Tropical Rain Forest For Species Diversity: An Investigation Using Arboreal Ants as an example

The arboreal ant communities of a primary lowland rain forest and three differently disturbed forests that lie close together forming an anthropogenic disturbance gradient were collected with insecticide fogging. Combined samples from all trees (87 foggings) comprised 153,504 ants sorted to 331 morphospecies. The primary forest ant fauna was characterized by high species richness and 53 foggings were necessary to collect communities representatively. Another 63 species of ants were found in the disturbed forests indicating a large regional species pool that might exceed 420 species of arboreal ants. Anthropogenic disturbance caused a change in the taxonomic composition, diversity and structure of ant communities. Community size was a predictor of species richness in the severely disturbed forest types but not in the old secondary or primary forest. Ant abundance had declined significantly in the disturbed forests and only 10% of the primary forest’s species were collected in the most disturbed forest type. In each of the secondary forests a change in the frequency distribution of species was observed and a small number of species had gained numerical dominance. Analysis of species associations indicates that the strength of species interactions changed with the degree of forest disturbance. These changes were still clearly recognizable after 40 years of forest regeneration despite optimal conditions for colonization from the adjacent primary forest, demonstrating that the time scale needed for forest recovery after anthropogenic disturbance is very long.     

The influence of anthropogenic disturbances on the structure of arboreal arthropod communities

In the framework of our research, aimed at understanding the processes structuring tropical arthropod communities, we investigated the changes occurring in tree crown communities of forests of different disturbance levels. These were a mixed dipterocarp primary lowland rain forest in Kinabalu National Park (in Sabah, Malaysia) and, some kilometres away, three forests of regeneration periods 5, 15, and 40 years following a clear-cut. These disturbed forest sites were adjacent to one another and merged into mature forest. From each forest at least ten individuals of one tree species were sampled using the fogging method. In the primary forest relative proportions of some arthropod taxa differed on the ordinal and familial level significantly within trees. The dominance of Formicidae was characteristic as was the almost complete lack of less mobile arthropods such as Lepidoptera larvae. In the five-year- old forest, differences in relative proportions among most taxa had almost disappeared. Formicidae abundances had declined drastically which coincided with an increase of Lepidoptera larvae. With progressing forest succession, arthropod communities increasingly converged on the pattern of primary forest, and total ant abundance as well as diversity increased significantly. Ant communities in the most disturbed forest were of low structural complexity, and to a large degree predictable in species arrangement, but became more and more unpredictable as the complexity of the forest increased. Several species of Coleoptera and non-formicine Hymenoptera occurred in high numbers in the youngest forest, contrasting with the mature forest where all species were typically rare. These changes may indicate a change in the structuring mechanisms from predominantly deterministic processes in disturbed forests to stochastic processes in mature forest.     

Community structure of arboreal caterpillars within and among four tree species of the eastern deciduous forest

Abstract.  1. A seasonally replicated experimental design was used to address the question of how differences within and among host tree species affect arboreal caterpillar communities.
2. Seasonal variation influenced caterpillar community composition most significantly, and the similarity among caterpillar assemblages did not necessarily follow the pattern of phylogenetic relatedness among host trees.
3. Species richness and abundance of caterpillars were higher on oaks and maples than on American beech. Diversity partitioning models revealed that β diversity was only occasionally greater or less than expected by chance alone.
4. When β diversity was significant, values tended to be greater than expected by chance among replicate trees within each species and lower than expected by chance among the four tree species.
5. Differences among trees appeared important for determining patterns of species presence/absence for rare species and influencing patterns of species dominance within caterpillar assemblages. Differences among tree species had a significant effect on overall lepidopteran community composition and mean species diversity (i.e. α diversity).
6. Because β diversity of caterpillars among host trees was lower than expected by chance, host specificity within the Lepidoptera may be less prevalent than thought previously.     

Arboreal arthropod biodiversity in woodlands. II. The pattern of recovery of diversity on Melaleuca linariifolia following defaunation

This study examines the level of isolation of arthropod faunas present on specimens of the endemic woodland tree Melaleuca linariifolia by investigating the recovery of faunas after defaunation using insecticide. One tree from each of 21 pairs of trees was sprayed at the beginning of the project (early April 1994). After predetermined periods, three test trees were resprayed along with matched control trees. A total of 95 154 arthropods were collected and sorted during the project. The number of species present on the trees recovered within 16 weeks of spraying, with common species recolonizing within a fortnight. The rarer species both of mobile (Diptera) and relatively sedentary (Araneae) taxa reappeared at similar rates. Complete recovery of numbers occurred by week 8 after spraying. Evenness (as Simpson’s D) recovered over the first 2 months; however, both the number of individuals and the evenness continued to diverge from the pattern seen on the control trees until the end of the study. While the rate of movement of individuals and species was such as to provide an apparently complete set of replacement species within several months of perturbation, the structure of the community found on the trees was still seriously disrupted after 1 year. Comparison of the suites of species originally found on the trees with those found in the respray samples and the control samples showed that the set of colonizing species was no more similar to the original fauna of the tree than it was to those on the control tree. The relatively rapid colonization of the trees by a suite of rare species – not necessarily those that were on particular trees before perturbation – indicates that rarity was due neither to inability of the species to colonize the trees nor to the suitability of the trees for these species. Recovery of rare species was to a level similar to that found on the control trees. That the divergences from the controls continued (in number of individuals and in evenness), implies a definite connection between the different faunas of a tree and their partial isolation from fauna communities on other trees. Whatever the forces that maintain suites of species on each tree, it is not the ability of the species to reach and colonize trees, nor certain attributes of a tree, that make it suitable only for a particular subset of the species available. Trees are not isolated entities but neither are they part of a fully integrated community, either chronologically or spacially, and issues of scale are also likely to be important in understanding and estimating the dynamics and factors regulating biodiversity levels.