Bruno Ferreira

Mr. Bruno Ferreira

orcid

Research Focus & Metrics

Academic Career Length

8Years (2019-Present)

(Calculated once Scilit publication data is synced: current year − year of first publication + 1)

Representative Publications

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3 October 2024 in Environmental Research: Climate
Verified
Journal Article
Open access
Carlos SouzaCarlos Souza
Carlos Souza
José MarengoJosé Marengo
José Marengo
BFBruno Ferreira
Bruno Ferreira
JRJúlia Ribeiro
Júlia Ribeiro
LSLucimara Wolfarth Schirmbeck
Lucimara Wolfarth Schirmbeck
MLMarcelo de Oliveira Latuf
Marcelo de Oliveira Latuf
The Amazon underwent a severe austral springtime drought attributed to the onset of El Niño in 2023 and the warmer North Atlantic, Indian, and North Pacific Oceans. The Amazon rivers, lakes, small streams, wetlands, and reservoirs quickly lowered their water level below historical records due to decreased rainfall and warmth in the region. Based on satellite imagery, this study presents the first estimate of the water loss extent in the 4.2 million km2 of the Brazilian Amazon biome (∼62% of the Amazon total biome) in 2023. We estimated the loss of 3.3 million hectares of surface water relative to 2022, with an overall accuracy of 92%. The surface water losses were concentrated in the states of Amazonas (59.4%) and Pará (25.5), adding up to 2.8 million hectares. The warmer and drier climate in the region affected the main rivers in the Amazon. Among them, the Solimões, Negro, Purus, Acre, and Branco suffered extreme drops in their levels in some regions, resulting in a high negative impact on the aquatic biodiversity, yet estimated only in local areas. A total of 1.14 million hectares of surface water loss (i.e. 35%) was detected within protected areas territories, affecting extractivist, indegenous, African-Brazilian, and fishing and traditional communities. Proximity analysis revealed that 75% of the 2023 surface water loss was within 25 km of small towns, 48% and 65.8% at 50 km from indigenous villages and urban areas, respectively. Our results reinforce people’s vulnerability to climate change, anticipating a plausible adverse impact scenario in the Amazon region and urging solutions to adaptation and mitigation. Therefore, an integrated monitoring system based on climate and water dynamics from satellite and ground stations is necessary to improve understanding of the problem for timing response of climatic change negative impacts.

5 November 2025 in Remote Sensing
Verified
Journal Article
Open access
PDF file
Carlos SouzaCarlos Souza
Carlos Souza
BFBruno Ferreira
Bruno Ferreira
IBIves Medeiros Brandão
Ives Medeiros Brandão
SRSandra Rios
Sandra Rios
JAJohn Fredy Aguilar-Brand
John Fredy Aguilar-Brand
Helga Correa WiederheckerHelga Correa Wiederhecker
Helga Correa Wiederhecker
The Amazon wetlands are the largest and most diverse freshwater ecosystem globally, characterized by various flooded vegetation and the Amazon River’s estuary. This critical ecosystem is vulnerable to land use changes, dam construction, mining, and climate change. While several studies have utilized remote sensing to map wetlands in this region, significant uncertainty remains, which limits the assessment of impacts and the conservation priorities for Amazon wetlands. This study aims to enhance wetland mapping by integrating existing maps, remote sensing data, expert knowledge, and cloud computing via Earth Engine. We developed a harmonized regional wetland classification system adaptable to individual countries, enabling us to train and build a random forest model to classify wetlands using a robust remote sensing dataset. In 2020, wetlands spanned 151.7 million hectares (Mha) or 22.0% of the study area, plus an additional 7.4 Mha in deforested zones. The four dominant wetland classes accounted for 98.5% of the total area: Forest Floodplain (89.0 Mha; 58.6%), Lowland Herbaceous Floodplain (29.6 Mha; 19.6%), Shrub Floodplain (16.7 Mha; 11.0%), and Open Water (14.1 Mha; 9.3%). The overall mapping accuracy was 82.2%. Of the total wetlands in 2020, 52.6% (i.e., 79.8 Mha) were protected in Indigenous Territories, Conservation Units, and Ramsar Sites. Threats to the mapped wetlands included 7.4 Mha of loss due to fires and deforestation, with an additional 800,000 ha lost from 2021 to 2024 due to agriculture, urban expansion, and gold mining. Notably, 21 Mha of wetlands were directly affected by both reduced precipitation and surface water in 2020. Our mapping efforts will help identify priorities for wetland protection and support informed decision-making by local governments and ancestral communities to implement conservation and management plans. As 47.4% of the mapped wetlands are unprotected and have some level of threats and pressure, there are also opportunities to expand protected areas and implement effective management and conservation practices.

9 December 2019 in Revista Sustinere
Verified
Journal Article
Open access
BFBruno Ferreira
Bruno Ferreira
DCDeborah Luciany Pires Costa
Deborah Luciany Pires Costa
ETErika De Oliveira Teixeira
Erika De Oliveira Teixeira
IVIgor Vieira
Igor Vieira
HNHILDO GIUSEPPE GARCIA CALDAS NUNES
HILDO GIUSEPPE GARCIA CALDAS NUNES
PSPaulo Jorge Souza
Paulo Jorge Souza
O açaizeiro é uma palmeira de grande importância socioeconômica a nível nacional e, principalmente, regional, tendo o estado do Pará como o maior produtor. A alta demanda de mercado proporcionou o surgimento crescente de plantios comerciais de açaí, sendo alguns manejados com irrigação. No entanto, pouco se sabe sobre o manejo adequado do açaí, por exemplo, quanto a sua demanda hídrica. Conhecer a dinâmica dos elementos atmosféricos e suas relações com a planta é imprescindível para o uso racional de técnicas, como a irrigação. O poder evaporante do ar (Ea) é um parâmetro de grande relevância para compreensão da evapotranspiração. Objetivou-se com este trabalho analisar a variabilidade de Ea em um cultivo de açaí nas condições climáticas de Castanhal-PA. Para tanto, foi calculado o Ea para o município de Castanhal, em que os dados de Temperatura (°C), Umidade Relativa (%) e Velocidade do vento (m s-1) foram obtidos a partir de uma torre micrometeorologica instalada e instrumentada em um açaizeiro comercial localizado nas dependências da Fazenda Escola de Castanhal (FEC). Foi calculado o déficit de pressão de vapor (DPV) a partir da metodologia de Tettens e o Ea foi obtido em função da velocidade do vento. Obteve-se o valor médio de Ea de 0,31 mm d-1 (±0,13) para o período analisado. Os resultados encontrados condizem com os da literatura e reafirmam a importância do estudo do poder evaporante do ar para a estimativa da evapotranspiração.

1 September 2022 in Revista Caatinga
Verified
Journal Article
Open access
ECErika DE Oliveira Teixeira DE Carvalho
Erika DE Oliveira Teixeira DE Carvalho
DCDeborah Luciany Pires Costa
Deborah Luciany Pires Costa
IVIgor Vieira
Igor Vieira
BFBruno Ferreira
Bruno Ferreira
HNHILDO GIUSEPPE GARCIA CALDAS NUNES
HILDO GIUSEPPE GARCIA CALDAS NUNES
PSPaulo Jorge Souza
Paulo Jorge Souza
Cowpea is a crop of great socioeconomic relevance for the populations of the North and Northeast of the country, and its low yield is commonly related to environmental stresses, especially water. The objective of this study was to evaluate the water stress index of cowpea, cultivar BR3 - Tracuateua, subjected to different irrigation levels (100, 50, 25 and 0% of ETc) in three reproductive phenological stages (R7, R8 and R9) in Castanhal-PA, Brazil. The experimental design was in randomized blocks, with six replications and four treatments corresponding to 100, 50, 25 and 0% of daily replacement of crop evapotranspiration, during the reproductive period, through an irrigation system. The surface temperature readings were made with infrared thermometer, during the reproductive stage. The smallest absolute temperature differences between canopy and air occurred in stages R7 and R8. The highest values of water stress index (CWSI) were verified when the plant was under water deficit, regardless of phenological stages. The effect of water deficit caused reductions in stomatal conductance of 58.82% (R7), 83.57% (R8) and 84.87% (R9), in leaf transpiration of 45.97% (R7), 64.21% (R8) and 65.90% (R9) and in the net photosynthetic rate of 40.75% (R7), 66.92% (R8) and 74% (R9). The CWSI varied with the availability of water, showing the highest value (0.75) in the treatment without irrigation, in the R8 stage. The CWSI proved to be a good indicator of the water status of the plant.