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An updated version of the checklist of birds of Brazil is presented, along with a summary of the changes approved by the Brazilian Ornithological Records Committee's Taxonomy Subcommittee since the first edition, published in 2015. In total, 1971 bird species occurring in Brazil are supported by documentary evidence and are admitted to the Primary List, 4.3% more than in the previous edition. Eleven additional species are known only from undocumented records (Secondary List). For each species on the Primary List, status of occurrence in the country is provided and, in the case of polytypic species, the respective subspecies present in Brazilian territory are listed. Explanatory notes cover taxonomic changes, nomenclatural corrections, new occurrences and other changes implemented since the last edition.Ninety species are added to the Primary List as a result of species descriptions, new occurrences, taxonomic splits and transfers from the Secondary List due to the availability of documentation.In contrast, eight species are synonymized or assigned subspecific status and thus removed from the Primary List. In all, 293 species are endemic to Brazil, ranked third among the countries with the highest rate of bird endemism. The Brazilian avifauna currently consists of 1742 residents or breeding migrants, 126 seasonal non-breeding visitors and 103 vagrants. The category of vagrants showed the greatest increase (56%) compared to the previous list, mainly due to new occurrences documented in recent years by citizen scientists. The list updates the diversity, systematics, taxonomy, scientific and vernacular nomenclature, and occurrence status of birds in Brazil.

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Inventários rápidos realizados em diferentes pontos no sul do Ceará e oeste de Pernambuco em julho e setembro de 2004 encontraram um total de 209 espécies de aves. A maior riqueza foi de espécies características das várias formações da Caatinga (99 espécies), seguidas por espécies de áreas abertas ou generalistas (65) e aves aquáticas (45). Não foi encontrado um padrão que associasse a similaridade entre áreas a um padrão geográfico. As espécies numericamente dominantes tendem a ser pequenos insetívoros que se alimentam em meio à vegetação baixa e granívoros como Columbidae e Coryphospingus pileatus. Generalistas como Cyanocorax cyanopogon também foram dominantes em alguns pontos. As caatingas muito alteradas ao redor de lagoas temporárias de Petrolina mostraram maior riqueza de espécies. De maneira geral a avifauna regional mostra poucas espécies de maior porte, como Cracidae e Psitacidae maiores, e aquelas dependentes de habitats mais estruturados, como grandes Dendrocolaptidae, refletindo tanto a exploração humana direta como a substituição de habitats de estrutura florestal por formações mais baixas e simples.
Rapid bird inventoires made in the Caatinga of southern Ceará and west Pernambuco in July and September 2004 found a total of 209 species. Birds characteristic of the different Caatinga habitats (from dense scrub to arboreal-arbustive forations) accounted for 99 species, followed by open habitats or generalist species (65) and waterbirds (45). We found no geographic pattern in area similarity. Numerically dominant species tend to be small insectivores feeding amid the lower vegetation and granivores such as Columbidae and Coryphospingus pileatus. Generalists such as Cyanocorax cyanopogon were also dominant in some áreas. The very disturbed scrub caatinga around temporary lagoons near Petrolina (Pernambuco) had the most species. The regional avifauna show few larger species such as Cracidae and Psitacidae, while birds associated to more arboreal, structured habitats such as the larger Dendrocolaptidae are also scarce or absent, refecting both direct human exploitation and the replacement of forest-like habitats by lower, less diverse scrub habitat

Flocks of seabirds attending commercial bottom long‐line fishing operations on the coastal shelf off southeastern Brazil show a greater species diversity during the summer than the winter (16 v 9 species), although the number of birds per flock tended to be greater during the cold season. During the summer, the Spectacled Petrel Procellaria aequinoctialis conspi‐cillata was the commonest species, followed by the Great Shearwater Puffinus gravis, Cory's Shearwater Calonectris diomedea, skuas Stercorarius spp. and the Yellow‐nosed AlbatrossDiomedea chlororhynchus. During the winter, the White‐chinned Petrel Procellaria aequin‐octialis, Yellow‐nosed Albatross and Black‐browed Albatross Diomedea melanophrys were jointly the commonest species. Marked differences in the relative abundance of species were observed between the different sampling periods, probably because of migratory movements but also because of seasonal shifts of the sea currents and the influence of cold fronts. Waters off southeastern Brazil are important feeding areas for some seabird populations nesting in the Tristan da Cunha and Gough group, especially for nonbreeding Spectacled Petrels and post‐breeding Yellow‐nosed Albatrosses.

Post-release monitoring data of reintroduced captive-bred birds can be utilized to help optimize future avian reintroduction programs. We present a case study of broad interest to reintroduction and conservation biologists interested in investigating movements and habitat use by reintroduced captive-bred birds. We used radio telemetry to monitor reintroduced captive-bred red-billed curassow Crax blumenbachii at a private reserve, Rio de Janeiro state, Brazil. During August 2006 and October 2008, 25 radio-tagged individuals (15 females and 10 males, all o30 months old) were monitored over a 25-month period. Evaluation of home-range size and habitat use revealed that captive-bred curassows should be released only into forest areas with adequate riverine habitat that are larger than the minimum home-range movements of the proposed population. Curassows also utilized pastureland, cultivated areas and secondary forests, suggesting that the proximity of release sites to such habitats may not be entirely detrimental for future reintroductions. Site fidelity for reintroduced birds was low, and there was a tendency for resident curassows to move away when new cohorts were released into the area. Determining how habitat characteristics, displacement by newly released cohorts, adjustments to their new surroundings or cohort social interactions influence post-release movements of resident birds at release sites over prolonged time frames would improve our knowledge on the impacts of releasing further captive-bred individuals into habitats with extant populations. Critically, the movement patterns of reintroduced curassows identified in this study demonstrate that avian post-release monitoring must be considered over an appropriate time frame and we highlight how different conclusions may be generated depending on the duration of post-release monitoring. It may take more than 2 years for reintroduced captive-bred sub-adults to become established following release and that post-release monitoring of similar duration may not be adequate for large avian species such as Cracids.

SummaryThe forests of the Angolan highlands are the smallest and most isolated of the Afromontane centres of endemism. Despite their high biodiversity value and small, fragmented extent of less than 200 ha, they remain entirely unprotected. Here we draw attention to their uniqueness and the threats to their conservation. We specifically highlight the importance of Mt Moco to bird conservation and describe current forest cover and condition. Sixty-four endemic/near-endemic species/subspecies and taxa with isolated populations are associated with the highlands of western Angola. All 19 forest-dependent taxa are among the 233 species recorded at Mt Moco, which include a rich diversity of montane specialists. Swierstra's Francolin Pternistis swierstrai is the only threatened endemic. In 2009, 10 of 30 forest patches at Mt Moco larger than 0.5 ha were surveyed for this species. It occurred in seven of these surveyed patches, at a mean minimum density of 0.95 pair ha À1 in forest patches . 1 ha. Based on extrapolations of this figure, we estimate a minimum of 75 pairs of Swierstra's Francolin at Mt Moco, and 185-420 pairs worldwide. Due to both limited range and small population size, we propose the species be up-listed from 'Vulnerable' to 'Endangered'. Total forest cover at Mount Moco in forest patches . 0.5 ha in size is currently 85 ha. This is c.40% of the total cover of Afromontane forest estimated for Angola in 1974. Remaining forest cover at Mt Moco is being eroded by bush fires, removal of wood for fire and construction material, and clearance for subsistence agriculture by the c.330 inhabitants of Kanjonde village. In order to preserve the forest of Mt Moco, we propose the implementation of a protected area and define its boundaries. A similar proposal was made in 1974 for the creation of the Mount Moco Special Reserve. ResumoAs florestas das terras altas de Angola formam o menor e mais isolado dos centros de endemismo de montanha de Á frica. Estas florestas abrigam uma biodiversidade ú nica. No entanto, em Angola, apesar deste habitat encontrar-se muito fragmentado e ocupar uma área total inferior a 200 ha, nenhuma parcela está protegida. Aqui destacamos a singularidade destas florestas e as ameaças que enfrentam. Em particular, destacamos a importância do Monte Moco para a conservação das aves e descrevemos a posição actual, área e qualidade da floresta que aqui permanece. Sessenta e quatro espécies/sub-espécies endémicas/quase-endémicas e espécies com populaçõ es isoladas estão associadas às terras altas de Angola ocidental. Destas, 19 dependem de floresta de montanha e todas elas estão presentes no Monte Moco, onde um total de 233 espécies foram registadas. O Francolim de Swierstra Pternistis swierstrai é a ú nica espécie endémica ameaçada. Em 2009, um censo desta espécie foi efectuado em 10 dos 30 fragmentos de floresta do Monte Moco com uma área superior a 0.5 ha. Esta espécie estava presente em sete dos fragmentos visitados, ocorrendo a uma densidade mínima média de 0.95 pares ha À1 nos fragmentos com...