RESUMO
Most Asteraceae species are pollinated by insects, mainly bees and butterflies, although pollination by birds has been documented and pollination by bats has been suggested for some species. Here, we investigated the pollination of Gongylolepis martiana, a species supposedly pollinated by bats. We assessed floral traits and visitors in a population of G. martiana in the Brazilian Amazon, measuring pollen removal from anthers and deposition on stigmas by diurnal and nocturnal visitors. Florets opened at dusk and lasted for 4 days, with the male phase starting on the first night and the female phase on the third night. Accumulated nectar per capitulum was 69.6 µl per night and sugar concentration was 15%. Nectar-feeding bats and hummingbirds contacted the sexual parts, but pollen removal and deposition were greater throughout the night than during the day, when Meliponini bees considerably reduced pollen availability. Other nocturnal visitors of G. martiana were rare, including nocturnal bees and moths that foraged for pollen and nectar, respectively. Our results support that nectarivorous bats are the main pollinators of G. martiana, confirming Vogel's hypothesis of bat pollination in Asteraceae, particularly in the genus Gongylolepis. Since anthesis and each sexual floral phase started in the evening, nectarivorous bats and diurnal bees caused additive priority effects, preventing hummingbirds from being efficient pollinators. The high density of flowering individuals of G. martiana in patches from white-sand forests likely increases bat attraction, while the small amount of nectar per plant favours cross-pollination.
Assuntos
Asteraceae , Borboletas , Quirópteros , Animais , Abelhas , Flores , PolinizaçãoRESUMO
A comprehensive study of material of the worldwide fungus gnat genus Manota Williston, sampled from the Allpahuayo-Mishana National Reserve in Peruvian Amazonia, was conducted. The following 16 species are described as new: M. aligera sp. n., M. aristoseta sp. n., M. calva sp. n., M. ciliata sp. n., M. exigua sp. n., M. digitata sp. n., M. flabellata sp. n., M. iquitosensis sp. n., M. limulata sp. n., M. micella sp. n., M. minutula sp. n., M. nuda sp. n., M. parvula sp. n., M. pauloides sp. n., M. pustulosa sp. n. and M. serrulata sp. n. In addition, the following 16 species are recorded: M. acuminata Jaschhof & Hippa, 2005, M. acutistylus Jaschhof & Hippa, 2005, M. anfracta Hippa & Kurina, 2013, M. appendiculata Hippa & Kurina, 2013, M. aristata Hippa & Kurina, 2013, M. bisulca Hippa & Kurina, 2013, M. diversiseta Jaschhof & Hippa, 2005, M. iota Hippa & Kurina, 2013, M. micula Hippa & Kurina, 2013, M. papillosa Hippa & Kurina, 2013, M. paula Hippa & Kurina, 2013, M. penicillata Jaschhof & Hippa, 2005, M. pisinna Hippa & Kurina, 2013, M. quantula Hippa & Kurina, 2013, M. spinosa Jaschhof & Hippa, 2005 and M. virgata Hippa & Kurina, 2013. Altogether 67 species of Manota are now known from the Neotropical region.
Assuntos
Dípteros , Distribuição Animal , Estruturas Animais , Animais , PeruRESUMO
Thirteen genera of Eucnemidae containing forty species were collected from the Iquitos region in Peru. Nine of the genera are new to the country: Rhagomicrus Fleutiaux, 1902, Adelorhagus Horn, 1890, Adelothyreus Chevrolat, 1867, Microrhagus Dejean, 1833, Dyscharachthis Blackburn, 1900, Heterotaxis Bonvouloir, 1871, Spinifornax Fleutiaux, 1926, Serrifornax Fleutiaux, 1926 and Maelodrus Fleutiaux, 1928. The previous eucnemid record from Peru contained eleven species in ten genera. Only one of the forty species caught, Entomophthalmusamericanus Bonvouloir, was previously known and described from the country. Dyscharachthis, Maelodrus and Adelorhagus are recorded from South America for the first time. Many of the collected species seem to favor white-sand forest as their habitat. Possible reasons for this are discussed. A list of eucnemids from Peru is included, containing taxa already recorded from the country and also taxa that are likely to occur there. A key to the Peruvian genera is included.
RESUMO
Soil heterogeneity is an important driver of divergent natural selection in plants. Neotropical forests have the highest tree diversity on earth, and frequently, soil specialist congeners are distributed parapatrically. While the role of edaphic heterogeneity in the origin and maintenance of tropical tree diversity is unknown, it has been posited that natural selection across the patchwork of soils in the Amazon rainforest is important in driving and maintaining tree diversity. We examined genetic and morphological differentiation among populations of the tropical tree Protium subserratum growing parapatrically on the mosaic of white-sand, brown-sand and clay soils found throughout western Amazonia. Nuclear microsatellites and leaf morphology were used to (i) quantify the extent of phenotypic and genetic divergence across habitat types, (ii) assess the importance of natural selection vs. drift in population divergence, (iii) determine the extent of hybridization and introgression across habitat types, (iv) estimate migration rates among populations. We found significant morphological variation correlated with soil type. Higher levels of genetic differentiation and lower migration rates were observed between adjacent populations found on different soil types than between geographically distant populations on the same soil type. PST -FST comparisons indicate a role for natural selection in population divergence among soil types. A small number of hybrids were detected suggesting that gene flow among soil specialist populations may occur at low frequencies. Our results suggest that edaphic specialization has occurred multiple times in P. subserratum and that divergent natural selection across edaphic boundaries may be a general mechanism promoting and maintaining Amazonian tree diversity.
Assuntos
Burseraceae/genética , Ecossistema , Genética Populacional , Seleção Genética , Solo , Teorema de Bayes , Análise por Conglomerados , Ecótipo , Fluxo Gênico , Deriva Genética , Hibridização Genética , Desequilíbrio de Ligação , Repetições de Microssatélites , Peru , Fenótipo , Folhas de Planta/anatomia & histologia , Árvores/genéticaRESUMO
The high tree diversity and vast extent of Amazonian forests challenge our understanding of how tree species abundance and composition varies across this region. Information about these parameters, usually obtained from tree inventories plots, is essential for revealing patterns of tree diversity. Numerous tree inventories plots have been established in Amazonia, yet, tree species composition and diversity of white-sand and terra-firme forests of the upper Rio Negro still remain poorly understood. Here, we present data from eight new one-hectare tree inventories plots established in the upper Rio Negro; four of which were located in white-sand forests and four in terra-firme forests. Overall, we registered 4703 trees > 10 cm of diameter at breast height. These trees belong to 49 families, 215 genera, and 603 species. We found that tree communities of terra-firme and white-sand forests in the upper Rio Negro significantly differ from each other in their species composition. Tree communities of white-sand forests show a higher floristic similarity and lower diversity than those of terra-firme forests. We argue that mechanisms driving differences between tree communities of white-sand and terra-firme forests are related to habitat size, which ultimately influences large-scale and long-term evolutionary processes.
A vasta extensão e a alta diversidade de árvores das florestas na Amazônia desafiam a nossa compreensão sobre como variam a composição e abundância de espécies arbóreas ao longo desta região. Informações sobre estes parâmetros, geralmente obtidas a partir de inventários florísticos, são fundamentais para análises sobre padrões de diversidade. Embora inúmeros inventários florísticos tenham sido estabelecidos na Amazônia, a composição de espécies e a diversidade de árvores das florestas de campinarana e de terra-firme, na região do alto Rio Negro, permanecem ainda pouco conhecidas. Aqui, apresentamos dados de inventários florísticos de oito parcelas de um hectare estabelecidas em florestas de campinarana e de terra-firme do alto Rio Negro. Ao todo, registramos 4.703 indivíduos com diâmetro à altura do peito > 10 cm pertencentes a 49 famílias, 215 gêneros e 603 espécies. As comunidades de árvores das florestas de campinarana e terra-firme do alto Rio Negro diferem entre si, sendo que as florestas de campinaranas são mais similares e menos diversas que as florestas de terra-firme. Sugerimos que os mecanismos que causam diferenças entre as comunidades arbóreas das florestas de campinarana e terra-firme são principalmente relacionados a diferenças do tamanho do habitat, isto porque o tamanho da área do habitat influencia processos evolutivos que ocorrem em grande escala temporal e espacial.
Assuntos
Árvores , FlorestasRESUMO
The high tree diversity and vast extent of Amazonian forests challenge our understanding of how tree species abundance and composition varies across this region. Information about these parameters, usually obtained from tree inventories plots, is essential for revealing patterns of tree diversity. Numerous tree inventories plots have been established in Amazonia, yet, tree species composition and diversity of white-sand and terra-firme forests of the upper Rio Negro still remain poorly understood. Here, we present data from eight new one-hectare tree inventories plots established in the upper Rio Negro; four of which were located in white-sand forests and four in terra-firme forests. Overall, we registered 4703 trees > 10 cm of diameter at breast height. These trees belong to 49 families, 215 genera, and 603 species. We found that tree communities of terra-firme and white-sand forests in the upper Rio Negro significantly differ from each other in their species composition. Tree communities of white-sand forests show a higher floristic similarity and lower diversity than those of terra-firme forests. We argue that mechanisms driving differences between tree communities of white-sand and terra-firme forests are related to habitat size, which ultimately influences large-scale and long-term evolutionary processes.
A vasta extensão e a alta diversidade de árvores das florestas na Amazônia desafiam a nossa compreensão sobre como variam a composição e abundância de espécies arbóreas ao longo desta região. Informações sobre estes parâmetros, geralmente obtidas a partir de inventários florísticos, são fundamentais para análises sobre padrões de diversidade. Embora inúmeros inventários florísticos tenham sido estabelecidos na Amazônia, a composição de espécies e a diversidade de árvores das florestas de campinarana e de terra-firme, na região do alto Rio Negro, permanecem ainda pouco conhecidas. Aqui, apresentamos dados de inventários florísticos de oito parcelas de um hectare estabelecidas em florestas de campinarana e de terra-firme do alto Rio Negro. Ao todo, registramos 4.703 indivíduos com diâmetro à altura do peito > 10 cm pertencentes a 49 famílias, 215 gêneros e 603 espécies. As comunidades de árvores das florestas de campinarana e terra-firme do alto Rio Negro diferem entre si, sendo que as florestas de campinaranas são mais similares e menos diversas que as florestas de terra-firme. Sugerimos que os mecanismos que causam diferenças entre as comunidades arbóreas das florestas de campinarana e terra-firme são principalmente relacionados a diferenças do tamanho do habitat, isto porque o tamanho da área do habitat influencia processos evolutivos que ocorrem em grande escala temporal e espacial.
RESUMO
Se presentan los patrones de floración y fructificación de 176 especies de plantas leñosas en bosques de suelos de arena blanca y arcillosos, cercanos a Iquitos. Las observaciones se realizaron cada dos semanas durante un periodo de 12 meses (Abril 2003 - Marzo 2004). En el sitio de estudio se establecieron 10 parcelas de 20 x 50 m, 5 parcelas en cada tipo de hábitat. La floración aconteció con mayor frecuencia de septiembre hasta diciembre, periodo en el cual hubo un incremento en la precipitación. Del mismo modo, hubo una tendencia de fructificación máxima desde noviembre hasta marzo, el cual coincidió con el periodo de mayor precipitación (octubre-diciembre), seguido de un periodo corto de menor precipitación (enero), terminando en febrero, periodo de mayor precipitación. La floración tuvo una duración de 0,5 a 9 meses y la fructificación de 1 a 10 meses. En el bosque de suelo arcilloso, la floración presentó su mayor pico en el periodo de menor precipitación de agosto-octubre con 22,2% de los individuos. Mientras que en el bosque de suelo de arena blanca el mayor pico de floración ocurrió en el periodo de mayor precipitación de noviembre-diciembre (19,3% de los individuos). La fructificación en los bosques de suelos arcilloso y de arena blanca presentaron mayores picos en el periodo de mayor precipitación de febrero-marzo con 20% y 23,5% de individuos, respectivamente, y en el periodo de mayor precipitación de noviembre-diciembre con 18,9% y 21,0% de los individuos, respectivamente. El índice de correlación entre la precipitación y temperatura con la floración y fructificación fueron en ambos casos positivos.
Patterns of flowering and fruiting of 176 species of woody plants in white-sand and clay forests near Iquitos, are presented. Observations were biweekly during a period of 12 months (April 2003 - March 2004). The study site were divided into 10 plots of 20 x 50 m, of which, 5 plots were established in each forest type. Flowering occurred most frequently from September to December, period in which there was an increase in precipitation. Similarly, there was a tendency for maximum fruiting from November to March. This period coincided with the season of greater precipitation (October-December), followed by a short interval period of less precipitation (January), ending in February, period of increased precipitation. Flowering lasted from 0,5 to 9 months and fruiting lasted from 1 to 10 months. In the clay forest, the flowering season showed its greater peak during the period with less rain (August-October), when 22,2% of the individuals were flowering. Whereas, in the white-sand forest, the greater peak of flowering occurred in the period of increased rain (November-December), with 19,3% of individuals flowering. On the other hand, the fruiting season in clay and white-sand forests showed two marked peaks. It tended to be greater during the rainiest period (February-March), with 20% and 23,5% of individuals, respectively, as well as during second highest rainy period (November-December) with 18,9% and 21% of individuals, respectively. The correlation index between the precipitation and temperature with the flowering and fruiting period were positive in both cases.