Similar seed preferences explain trophic ecology of functionally distinct, but co-occurring and closely related harvester ants.

To understand how food resource use and partitioning by closely related species allows local coexistence, it is key to determine whether a species' diet reflects food availability or food preferences. Here, we analysed the diets, seed selection, and seed preferences of three closely related harvester ants: Messor barbarus, M. bouvieri, and M. capitatus. Sympatric within a Mediterranean shrubland, these species differ in foraging behaviour and worker polymorphism. For 2 years, we studied the ants' diets and seed selection patterns as well as the local availability of seeds. Additionally, we performed a seed-choice experiment using a paired comparison design, offering the ants seeds from eight native plant species. The three ant species had the same general diet, which was primarily granivorous. Although they all consumed a wide variety of seeds, they mostly selected seeds from a small subset of plant species. Despite their morphological and behavioural differences, the ants displayed similar seed preferences that were highly consistent with their diets and seed selection patterns. Our results support the idea that the trophic ecology of these three harvester ants is driven by similar seed preferences rather than by their morphological and behavioural differences. Seed diversity and abundance were high near the ants' nests, suggesting that seed availability is not limiting and could in fact favour local species coexistence.

Competitive Effects Hinder the Recolonization of Native Species in Environments Densely Occupied by One Invasive Exotic Species.

The responses of native plants to competition with invasive plants depend mainly on the density of the invasive plants and on the ability of the native plants to compete for resources. In this study, we tested the influence of the invasive exotic Urochloa arrecta (Poaceae) on the early colonization of two native species (Pontederia cordata and Leersia hexandra) of aquatic macrophytes. Our hypotheses were (i) the competitive effects of U. arrecta on the native species P. cordata and L. hexandra are density-dependent and that (ii) these species respond differently to competitive interactions with the invasive species. We conducted the experiments in a greenhouse and in the field, in a tropical reservoir. The biomass of U. arrecta (ranging from 206.2 to 447.1 g) was manipulated in the greenhouse in trays with different densities. After the establishment of the invasive species, we added P. cordata and L. hexandra propagules to each tray. In the field, a propagule of P. cordata was planted in 36 sites with different densities of U. arrecta. The biomass and length of the natives and the biomass of the invasive species were measured in the greenhouse and in the field experiments. The biomass and length of the native plants decreased with increasing biomass of the exotic species in both experiments, showing that the competition between U. arrecta and native species depends on the density of the exotic species. The root:shoot ratio of L. hexandra decreased with increasing U. arrecta biomass, but the opposite occurred for P. cordata. These results indicate that native species exhibit different strategies of biomass allocation when interacting with U. arrecta. The strong competitive effects of U. arrecta and the different responses of the native species help to explain the reduced diversity of native macrophytes observed in sites colonized by U. arrecta. The results also suggest that in a scenario of dominance of exotic species, recolonization by native macrophytes is unlike to occur naturally and without human interventions that reduce the biomass of the exotic species.

Do grandparents compete with or support their grandchildren? In Guatemala, paternal grandmothers may compete, and maternal grandmothers may cooperate.

Previous research has found that the presence of grandparents, particularly grandmothers, is often positively associated with child survival. Little research has explored the potential mechanisms driving these associations. We use data from rural Guatemala to test whether contact with and direct investment (advice and financial) from grandparents is associated with child health, proxied by height. Our results demonstrate the complexity of family relationships and their influence on child health, suggesting that both cooperative and competitive relationships exist within the family. The clearest evidence we find for grandparental influence is that having a living paternal grandmother tends to be negatively associated with child height. By contrast, contact with maternal kin appears broadly to be beneficial for child height, although these relationships are weaker. These patterns are mirrored in maternal body mass index, suggesting grandparental influence acts partly through maternal health. These findings support the hypotheses that, under conditions of limited resources, family relationships may be competitive within the family lineage which shares the same resource base, but cooperative when there are few costs to cooperation. Finally, financial assistance from maternal grandfathers is positively correlated with infant length but negatively with the height of older children, perhaps because the receipt of financial support is an indication of need. The provision of advice shows no associations with child height.

Bean Type Modifies Larval Competition in Zabrotes subfasciatus (Chrysomelidae: Bruchinae).

Larval competition is particularly prevalent among grain beetles that remain within their mother-selected grain throughout development, and the behavioral process of competition is usually inferred by the competition outcome. The Mexican bean weevil Zabrotes subfasciatus (Boheman) is subjected to resource availability variation because of the diversity of common bean types and sizes, from small (e.g., kidney beans) to large (e.g., cranberry beans). The competition process was identified in the Mexican bean weevil reared on kidney and cranberry beans by inference from the competition outcome and by direct observation through digital X-ray imaging. Increased larval density negatively affected adult emergence in kidney beans and reduced adult body mass in both kidney and cranberry beans. Developmental time was faster in cranberry beans. The results allowed for increased larval fitness (i.e., higher larval biomass produced per grain), with larval density reaching a maximum plateau >5 hatched larvae per kidney bean, whereas in cranberry beans, larval fitness linearly increased with density to 13 hatched larvae per bean. These results, together with X-ray imaging without evidence of direct aggressive interaction among larvae, indicate scramble competition, with multiple larvae emerging per grain. However, higher reproductive output was detected for adults from lower density competition with better performance on cranberry beans. Larger populations and fitter adults are expected in intermediate larval densities primarily in cranberry beans where grain losses should be greater.

Abelhas africanizadas Apis mellifera scutellata Lepeletier, 1836 (Hymenoptera: Apidae: Apinae) exploram recursos na floresta amazônica?

The African honeybees (Apis mellifera scutellata) were introduced accidentally to Brazil in 1956 where it subsequently interbred with other subspecies of European honeybee here introduced in the 19th century. This resulted in hybrids with predominantly African honeybee characteristics, such as higher capacity of swarming and survival in inhospitable conditions, allowing them to adapt quickly and expand throughout nearly of the Americas. Moreover, to date there is much controversy about the probable impact of these bees, called Africanized honey bees, on native bees. In the Americas, Africanized honeybees are limited to regions of low altitude and cool winters, and in Brazil they occur principally in urban areas, and open or disturbed vegetation, not occurring in the interior of dense forest such as the Amazon Forest. We offered various kinds of bait in the interior of continuous forest, and in forest fragments to verify if Africanized honeybees would be capable of penetrate in it. No Africanized honeybee workers visited any baits in continuous forest or in forest fragments, but they did so in deforested/open areas. This result indicates that there is no possibility of source competition between Africanized and native bees within Amazon forest, and also indicates that large-scale beekeeping is unlikely to succeed in this region, because forest is not explored by Africanized bees.

As abelhas africanas (Apis mellifera scutellata) foram trazidas para o Brasil na década de 1950 e, por acidente, cruzaram-se com outras subespécies de abelhas melíferas européias introduzidas no século XIX. Isso proporcionou o surgimento de híbridos com características predominantes das abelhas africanas, tais como rusticidade e maior capacidade de enxamear, o que lhes permitiu uma rápida adaptação e expansão por quase todo continente americano. Até hoje existem controvérsias se essas abelhas, denominadas africanizadas, causam algum impacto sobre a fauna de abelhas nativas. Nas Américas, as africanizadas estão restritas a regiões de baixas altitudes e de invernos amenos; no Brasil, ocorrem principalmente em áreas urbanas e formações vegetacionais abertas ou adulteradas, sendo dificilmente vistas ou coletadas no interior de florestas densas como a amazônica. Diante dessa observação, diversas iscas foram disponibilizadas no interior de fragmentos de florestas e de florestas contínuas na Amazônia central, para testar se operárias de abelhas africanizadas seriam capazes de penetrar nos mesmos. Nenhuma operária foi vista visitando as iscas na floresta contínua ou mesmo nos fragmentos de floresta, ocorrendo visitas somente nas áreas desmatadas e capoeiras próximas. Esse resultado, além de indicar a inexistência de competição por recursos com as abelhas nativas no interior da floresta amazônica, também indica que uma apicultura em grande escala na região seria inviável, uma vez que a floresta não é sequer visitada por essas abelhas.