O presente trabalho foi realizado em uma zona ripária no período de outubro de 2000 a setembro de 2001, em uma parcela representativa de mata ciliar com vegetação do tipo "Floresta Estacional Semidecidual", localizada no centro-sul do Estado de São Paulo. A produção total de serapilheira foi de 10.646,0 kg.ha-1.a-1. A maior deposição de serapilheira e nutrientes ocorreu no fim da estação seca. A transferência total de macronutrientes foi de 217,76 kg.ha-1 de N, 11,55 kg.ha-1 de P, 52,79 kg.ha-1 de K, 199,80 kg.ha-1 de Ca e 38,70 kg.ha-1 de Mg. A serapilheira acumulada foi estimada em 6.227,25 kg.ha-1, a estimativa da taxa instantânea de decomposição (K), de 1,71; e o tempo necessário para o desaparecimento de 50 e 95% da serapilheira produzida, 150 e 639 dias, respectivamente.

The broad negative consequences of habitat degradation on biodiversity have been studied, but the complex effects of natural–agricultural landscape matrices remain poorly understood. Here we used stable carbon and nitrogen isotopes to detect changes in mammal resource and habitat use and trophic structure between preserved areas and human-modified landscapes (HMLs) in a biodiversity hot spot in South America. We classified mammals into trophic guilds and compared resource use (in terms of C3- and C4-derived carbon), isotopic niches, and trophic structure across the 2 systems. In HMLs, approximately one-third of individuals fed exclusively on items from the agricultural matrix (C4), while in preserved areas, ∼68% depended on forest remnant resources (C3). Herbivores, omnivores, and carnivores were the guilds that most incorporated C4carbon in HMLs. Frugivores maintained the same resource use between systems (C3resources), while insectivores showed no significant difference. All guilds in HMLs except insectivores presented larger isotopic niches than those in preserved areas. We observed a complex trophic structure in preserved areas, with increasing δ15N values from herbivores to insectivores and carnivores, differing from that in HMLs. This difference is partially explained by species loss and turnover and mainly by the behavioral plasticity of resilient species that use nitrogen-enriched food items. We concluded that the landscape cannot be seen as a habitat/nonhabitat dichotomy because the agricultural landscape matrix in HMLs provides mammal habitat and opportunities for food acquisition. Thus, favorable management of the agricultural matrix and slowing the conversion of forests to agriculture are important for conservation in this region.

Scientists have long been trying to understand why the Neotropical region holds the highest diversity of birds on Earth. Recently, there has been increased interest in morphological variation between and within species, and in how climate, topography, and anthropogenic pressures may explain and affect phenotypic variation. Because morphological data are not always available for many species at the local or regional scale, we are limited in our understanding of intra‐ and interspecies spatial morphological variation. Here, we present the ATLANTIC BIRD TRAITS, a data set that includes measurements of up to 44 morphological traits in 67,197 bird records from 2,790 populations distributed throughout the Atlantic forests of South America. This data set comprises information, compiled over two centuries (1820–2018), for 711 bird species, which represent 80% of all known bird diversity in the Atlantic Forest. Among the most commonly reported traits are sex (n = 65,717), age (n = 63,852), body mass (n = 58,768), flight molt presence (n = 44,941), molt presence (n = 44,847), body molt presence (n = 44,606), tail length (n = 43,005), reproductive stage (n = 42,588), bill length (n = 37,409), body length (n = 28,394), right wing length (n = 21,950), tarsus length (n = 20,342), and wing length (n = 18,071). The most frequently recorded species are Chiroxiphia caudata (n = 1,837), Turdus albicollis (n = 1,658), Trichothraupis melanops (n = 1,468), Turdus leucomelas (n = 1,436), and Basileuterus culicivorus (n = 1,384). The species recorded in the greatest number of sampling localities are Basileuterus culicivorus (n = 243), Trichothraupis melanops (n = 242), Chiroxiphia caudata (n = 210), Platyrinchus mystaceus (n = 208), and Turdus rufiventris (n = 191). ATLANTIC BIRD TRAITS (ABT) is the most comprehensive data set on measurements of bird morphological traits found in a biodiversity hotspot; it provides data for basic and applied research at multiple scales, from individual to community, and from the local to the macroecological perspectives. No copyright or proprietary restrictions are associated with the use of this data set. Please cite this data paper when the data are used in publications or teaching and educational activities.

flora sureveys are fundamental for the implementation of management plans and measures for the conservation of the biome. The Amadeu Botelho Ecological Reserve (ERAB) is a Private Reserve of Natural Heritage (PRNH) that contains a preserved fragment of Atlantic Forest whose mammal fauna has yet to be thoroughly studied. Hence, the present study surveyed the mammalian fauna of the ERAB and evaluated the influence of the farm's plantations and its proximity to the urban center on these mammals. Materials and Methods Study site The study area is the Ecological Reserve Amadeu Botelho (ERAB), one Private Reserve of Natural Heritage (PRNH) created through the Ordinance No. 19 ICMBio (Instituto Chico Mendes de Conservação da Biodiversidade) in 2000. It is owned by the Santo Antonio Ipês farm located in the municipality of Jaú (22°18′ S, 48°31′ W), in the central-western region of the state of São Paulo, in southeastern Brazil. The farm was acquired by Arruda Botelho family in the late 19th century (Conselho Nacional da Reserva da Biosfera da Mata Atlântica 2008). The farm grows various crops such as sugarcane, corn, sunflowers, oranges, as well as species of the genus Cordia, medicinal passion fruit, peaches and coffee. These plantations surround the entire forest fragment, giving it a clear cut and elongated appearance (Figure 1). Several dirt roads cut through these plantations, which are used to transport harvested crops. In addition, two roads cut

No abstract