Pervasive gaps in Amazonian ecological research

Biodiversity loss is one of the main challenges of our time, and attempts to address it require a clear understanding of how ecological communities respond to environmental change across time and space. While the increasing availability of global databases on ecological communities has advanced our knowledge of biodiversity sensitivity to environmental changes, vast areas of the tropics remain understudied. In the American tropics, Amazonia stands out as the world's most diverse rainforest and the primary source of Neotropical biodiversity, but it remains among the least known forests in America and is often underrepresented in biodiversity databases. To worsen this situation, human-induced modifications may eliminate pieces of the Amazon's biodiversity puzzle before we can use them to understand how ecological communities are responding. To increase generalization and applicability of biodiversity knowledge, it is thus crucial to reduce biases in ecological research, particularly in regions projected to face the most pronounced environmental changes. We integrate ecological community metadata of 7,694 sampling sites for multiple organism groups in a machine learning model framework to map the research probability across the Brazilian Amazonia, while identifying the region's vulnerability to environmental change. 15%–18% of the most neglected areas in ecological research are expected to experience severe climate or land use changes by 2050. This means that unless we take immediate action, we will not be able to establish their current status, much less monitor how it is changing and what is being lost

Consistent patterns of common species across tropical tree communities

Trees structure the Earth’s most biodiverse ecosystem, tropical forests. The vast number of tree species presents a formidable challenge to understanding these forests, including their response to environmental change, as very little is known about most tropical tree species. A focus on the common species may circumvent this challenge. Here we investigate abundance patterns of common tree species using inventory data on 1,003,805 trees with trunk diameters of at least 10 cm across 1,568 locations1,2,3,4,5,6 in closed-canopy, structurally intact old-growth tropical forests in Africa, Amazonia and Southeast Asia. We estimate that 2.2%, 2.2% and 2.3% of species comprise 50% of the tropical trees in these regions, respectively. Extrapolating across all closed-canopy tropical forests, we estimate that just 1,053 species comprise half of Earth’s 800 billion tropical trees with trunk diameters of at least 10 cm. Despite differing biogeographic, climatic and anthropogenic histories7, we find notably consistent patterns of common species and species abundance distributions across the continents. This suggests that fundamental mechanisms of tree community assembly may apply to all tropical forests. Resampling analyses show that the most common species are likely to belong to a manageable list of known species, enabling targeted efforts to understand their ecology. Although they do not detract from the importance of rare species, our results open new opportunities to understand the world’s most diverse forests, including modelling their response to environmental change, by focusing on the common species that constitute the majority of their trees

Padrões de floração e frutificação de árvores da Amazônia Maranhense Flowering and Fruiting Patterns of the Maranhense Amazon Rainforest Trees

Estudos fenológicos em nível de comunidades podem facilitar a compreensão do comportamento das espécies diante de alterações nos ecossistemas, além de refletir a distribuição anual de tipos específicos de recursos. Este trabalho buscou definir os padrões gerais e a sazonalidade de floração e frutificação de uma comunidade em duas áreas de floresta na Amazônia Maranhense, uma não perturbada e outra submetida a corte seletivo. A vegetação corresponde às matas de cipós das florestas amazônicas, alternando matas densas e abertas, de alta biomassa. Valores médios anuais de temperatura variam entre 24,5º C e 26,0º C, e entre 1400 mm e 1800 mm de precipitação, com um período seco de 5 a 6 meses, de junho a novembro. Foram analisadas a floração e a frutificação de 89 espécies arbóreas, de agosto de 1994 a junho de 1996. As espécies foram agrupadas em: árvores do sub-dossel, árvores do estrato superior e árvores que ocorrem em ambos os estratos. Foi feita comparação entre grupos (estratos, tipos de floresta e mecanismos de dispersão) e possíveis correlações com a precipitação foram investigadas. Quinze espécies estudadas foram exclusivas do estrato inferior e 63 do estrato superior da floresta; 17 espécies foram registradas apenas na mata nativa e 37 apenas na mata manejada. A maioria das espécies é zoocórica (62,9 %). A floração e a frutificação ocorreram durante todo o ano, com pico de floração de outubro a dezembro e picos de frutificação de março a julho e de outubro a dezembro. Os resultados obtidos demonstram uma grande sincronia na floração e frutificação dos indivíduos, e confirmam a relação entre esses processos e a variação na precipitação ao longo do ano, e que plantas de ambientes diferenciados exibem comportamentos fenológicos diferentes. Os padrões observados foram semelhantes entre as áreas e a outros estudos na Amazônia.<br>Community level phonological studies can facilitate the understanding of species behavior as a result of ecosystem changes, further reflecting on the annual allotment of specific resources. The aim of the present study was to define the general patterns, flowering and fruiting seasonality from a community in two forest areas of the Maranhense Amazon Rainforest: a non-disturbed area and another submitted to selective logging. The vegetation is composed of Amazon forest lianas alternating between dense and open high biomass forest. Average annual temperature varies between 24.5O C and 26.0O C, with precipitation ranging from 1400 mm to 1800 mm, and a dry season between June and November. Flowering and fruiting of 89 species were analyzed from August 1994 to June 1996. The species were grouped as follows: sub-dossal, upper strata, and trees occurring in both strata. Comparison was made between groups (strata, types of forest and mechanisms for dispersal) and possible correlations with rainfall were investigated. Fifteen studied species were solely from the lower strata, and 63 from the upper forest strata; 17 species were recorded only in native forest and 37 in managed forest. Most species (62.9 %) is zoochorous. Flowering and fruiting take place throughout the year with flowering peak from October to December and fruiting peaks from March to July and from October to December. The results showed a great synchrony in flowering and fruiting of individuals, and confirm the relationship between these cases and the variation in rainfall throughout the year, and that plants of different environments exhibit phonological behavior different. The observed flowering and fruiting patterns were similar between the areas and comparable to other studies in the Amazon Rainforest