O mico-leão-dourado ( Leontopithecus rosalia) como dispersor de sementes na Reserva Biológica União/IBAMA, Rio das Ostras, RJ.

Lapenta, Marina Janzantti

doi:10.11606/d.41.2002.tde-30092004-094442

Cited by 8 publications

(11 citation statements)

References 106 publications

(161 reference statements)

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“…The daily activity periods found in this study are in agreement with results of previous studies on golden lion tamarins in the UBR: 9-12 h (Kierulff 2000), 10.5 h (Lapenta 2002) and 10.5 h (Procó pio de Oliveira 2002). Other species of the Callitrichidae are active approximately 8-12 h per day (Kleiman et al 1988, Snowdon and Soini 1988, Soini 1988, Stevenson and Rylands 1988.…”

Section: Daily Activitysupporting

confidence: 92%

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Daily activity period, home range and sleeping sites of golden lion tamarins (Leontopithecus rosalia) translocated to the União Biological Reserve, RJ-Brazil

Lapenta¹,

Oliveira²,

Nogueira-Neto³

2007

Mammalia

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Golden lion tamarins (Leontopithecus rosalia) are known to sleep in tree holes as a means of protection against predators. The aim of this study was to compare the activity period of the diurnal golden lion tamarins with the home range of each group, and the sleeping sites used by tamarins in the Uniã o Biological Reserve. Two groups (Geni and SJ2) were followed monthly from April 2003 to March 2004, for a total of 712 h. The daily distance and the home range of the groups were estimated, the trees used as sleeping sites were marked with numbered tags, and the habitat and the positions of the trees were mapped. During the study, the mean daily activity period was 10.30 h. The SJ2 group had a home range of 96.22 ha and 21 different sleeping sites, and the Geni group had a home range of 72.52 ha and nine different tree hole sleeping sites. The daily activity of golden lion tamarins varied seasonally and was associated with photoperiod and temperature. The size of the home range may be influenced by the occurrence and interaction with neighboring groups.

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Section: Daily Activitysupporting

confidence: 92%

“…The daily activity of golden lion tamarins varies seasonally and is associated with photoperiod and temperature (Passos 1997, Lapenta 2002, Lapenta et al 2003. These animals are more active in the wet season, due to the long days and hot temperatures.…”

Section: Daily Activitymentioning

confidence: 99%

Daily activity period, home range and sleeping sites of golden lion tamarins (Leontopithecus rosalia) translocated to the União Biological Reserve, RJ-Brazil

Lapenta¹,

Oliveira²,

Nogueira-Neto³

2007

Mammalia

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“…In REBIO União, 57 plant species have been recorded as food sources for the golden-lion tamarin (Leontopithecus rosalia Linnaeus, 1766). Four of these plant species are known to host galls -Inga edulis, Myrcia sp., Pourouma sp., and Simarouba amara (Lapenta 2002) -all of which are cryptic, except for one morphotype on Myrcia sp., which is reddish. We observed color change in a single gall morphotype, which changed from green to yellow.…”

Section: Discussionmentioning

confidence: 99%

Insect galls of the Reserva Biológica União, Rio de Janeiro, Brazil

Maia¹,

Siqueira²

2020

Biota Neotrop.

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Several inventories of insect galls have been performed in the Atlantic Forest of Rio de Janeiro, mostly in restingas, whereas the other phytophysiognomies remain poorly sampled. The present study inventoried the insect galls of Reserva Biológica União (RJ), a protected area comprising mainly Ombrophilous Forest. Field work was performed every two months from January to October, 2013. Insect galls were collected, photographed, characterized and transported to the laboratory. Adults were obtained by rearing and immature stages by gall dissection. The insects were deposited in the Cecidomyiidae Collection of the Museu Nacional. A total of 153 gall morphotypes were found on plants representing 37 plant families, 69 genera, 55 species and 53 morphospecies. Among them, two plant genera and five species were reported for the first time as host plants in Ombrophilous Forest. REBIO União showed little similarlity of host plant species and insect gall morphotypes when compared with other investigated Ombrophilous Forest areas. The leaf was the most attacked plant organ as expected. Asteraceae, Bignoniaceae, Fabaceae and Myrtaceae, and Mikania (Asteraceae) and Myrcia (Myrtaceae) were the richest host families and genera, respectivey, in number of gall morphotypes, all previously indicated as superhosts by other Brazilian Ombrophilous Forest inventories, except Bignoniaceae. Their great species richness may be related to their great gall richness, adding evidence in support of the taxon size hypothesis. Fusiform and globose galls were the most frequent, green was the predominant color, and most morphotypes did not present an indumentum. The highest gall richness was recorded in June and August. The gallers were distributed among Diptera (Cecidomyiidae), Lepidoptera, Hymenoptera, Hemiptera and Thysanoptera, with the first being predominant, following a global pattern. Eight gall-inducing species are recorded for the first time in REBIO União and four in Ombrophilous Forest. About 25% of the gall morphotypes were occupied by dwellers other than those that created the gall. They comprised parasitoids (Hymenoptera), inquilines (Diptera: Sciaridae and Muscomorpha, Hemiptera, and Lepidoptera) and successors (Psocoptera, mites, and Hymenoptera: Formicidae). Although these taxa were previously reported by Brazilian inventories of insect galls, 12 new association with plants are recorded. The amount of new records reinforces the importance of inventories.Resumo: Vários inventários de galhas de insetos vem sendo desenvolvidos no estado do Rio de Janeiro, principalmente em restingas, enquanto as outras fitofisionomias permanecem pouco estudadas. O presente estudo inventariou as galhas de insetos da Reserva Biológica União (RJ), uma área protegida ocupada principalmente por Floresta Ombrófila. Trabalhos de campo foram realizados a cada dois meses de janeiro a outubro de 2013. Galhas de insetos foram coletadas, fotografadas, caracterizadas e transportadas para o laboratório. Adultos foram obtidos por criação e os imaturos pela dissecção...

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“…Segundo McConkey 2000, os primatas possuem importância como agentes dispersores, pois ingerem grande número de sementes dos frutos que consomem que permanecem viáveis após serem eliminadas nas fezes (Chapman, 1989). Todavia, de acordo com Figueiredo (1993) e Lapenta (2002), em geral os primatas não apresentam um efeito consistente na germinação de sementes, pois beneficiam apenas algumas espécies, enquanto prejudicam a porcentagem e/ou o tempo da germinação de outras. Lapenta (2002) estudou o papel do micoleão-dourado (Leontopithecus rosalia) como dispersor de sementes, na reserva ecológica União/IBAMA, Rio das Ostras-RJ, e verificou que este animal é responsável pela dispersão de 57 espécies de árvores e de pelo menos 17 famílias.…”

Section: Dispersão De Sementes Por Mamíferos (Mamaliocoria)unclassified

Dispersão natural de sementes: importância, classificação e sua dinâmica nas pastagens tropicais

Deminicis

Vieira²,

Araújo

et al. 2008

ARCH ZOOTEC

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A propagação de plantas pela dispersão de sementes é reconhecida como um dos fatores fundamentais que afetam o recrutamento das plantas e é um importante passo do ciclo reprodutivo da maioria delas. A dispersão reduz os níveis de predação nas proximidades dos adultos da mesma espécie, aumenta as chances de germinação das sementes e estabelece novos habitats favoráveis a colonização. Além disso, a dispersão de sementes também gera a distribuição espacial dos indivíduos adultos da população. Embora seja reconhecida a importância da ressemeadura natural na renovação e persistência de espécies em pastagens, o entendimento do processo de dispersão sob nova perspectiva dentro dos modernos modelos de produção, que se pautam na sustentabilidade, onde temos, lado a lado, animais silvestres e produção pecuária baseada em pastagens é um assunto pouco conhecido. Com essa revisão, objetivou-se traçar a trajetória dos estudos sobre dispersão de sementes, com ênfase nos sistemas de classificação, os tipos, os dispersores, o processo de dispersão de sementes entre habitats, avaliação do potencial de dispersão de espécies vegetais através de ruminantes e as aplicações e limitações atuais da dispersão de sementes, e assim contribuir para a construção dessa nova concepção de desenvolvimento baseada na sustentabilidade dos sistemas de produção agropecuários.

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O mico-leão-dourado ( Leontopithecus rosalia) como dispersor de sementes na Reserva Biológica União/IBAMA, Rio das Ostras, RJ.

Cited by 8 publications

References 106 publications

Daily activity period, home range and sleeping sites of golden lion tamarins (Leontopithecus rosalia) translocated to the União Biological Reserve, RJ-Brazil

Daily activity period, home range and sleeping sites of golden lion tamarins (Leontopithecus rosalia) translocated to the União Biological Reserve, RJ-Brazil

Insect galls of the Reserva Biológica União, Rio de Janeiro, Brazil

Dispersão natural de sementes: importância, classificação e sua dinâmica nas pastagens tropicais

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