The partial or complete loss of vegetation cover triggers an increase in surface runoff, erosion, and sedimentation of water bodies, including reservoirs for hydroelectric power generation, reducing their life expectancy. To control or mitigate this issue, ecological restoration interventions should prioritize the recovery of areas most vulnerable to these processes, such as springs. Conversely, wildfires cause damage to vegetation cover and hinder ecological restoration and/or natural regeneration processes. Therefore, this study aimed to identify - with the aid of Geographic Information Systems - the temporal and spatial likelihood of fire occurrences in spring recharge areas undergoing ecological restoration and contributing to hydroelectric reservoirs in southern Minas Gerais, Brazil. The findings indicated that the months with the highest probability of wildfire occurrences were August and September (accounting for 66% of cases), requiring increased attention to prevention efforts. Furthermore, locations most susceptible to fires (steeper slopes, more flammable vegetation, and higher anthropogenic use) should be treated as priorities for both prevention and ecological restoration actions

A perda parcial ou total da cobertura vegetal desencadeia um aumento do escoamento superficial, erosão e assoreamento de corpos hídricos, entre eles os reservatórios para a geração de energia hidroelétrica, reduzindo sua expectativa de vida útil. Para tentar controlar ou corrigir este problema, intervenções de restauração ecológica devem priorizar a recuperação de áreas mais frágeis a estes processos, como as nascentes. Por outro lado, a ocorrência de incêndios promove danos à cobertura vegetal e inibem os processos de restauração ecológica e/ou regeneração natural. Desta forma, o objetivo deste estudo foi identificar - com o auxílio de Sistemas de Informações Geográficas - a época mais provável e os locais mais susceptíveis aos incêndios, em áreas de recarga de nascentes sob processo de restauração ecológica e que são contribuintes de reservatórios hidroelétricos no sul de Minas Gerais, Brasil. Os resultados demonstraram que os meses de maior probabilidade de ocorrências de incêndios florestais foram agosto e setembro (66% dos casos), o que exigirá maior atenção quando das ações de prevenção. Bem assim, que os locais mais susceptíveis à ocorrência de incêndios (maior inclinação, vegetação mais inflamável e maior uso antrópico) necessitarão ser tratados como prioritários, tanto para ações de prevenção quanto de restauração ecológica

Abstract Forest burning susceptibility mapping is a tool to mitigate wildfires, with several methods to develop them. This study aimed to compare the Analytic Hierarchy Process (AHP), Multiple Linear Regression (MLR), and Random Forest (RF) methods for mapping. Several variables were used to generate the maps. For MLR and RF methods, fire frequency between 1990 and 2010 was used as the response variable in the models. To validate the methods (AHP, MLR and RF), fire data between 2011 and 2018 were used in four stages. RF was the best method employed. Correct and incorrect values for this method were 74% and 26% and AUC 0.66. The sensitivity and specificity for the highest risk class were 31% and 96%. The low sensitivity values can be attributed to the randomness attributed to anthropic fire. The high specificity values point to a good separation of the higher risk class compared to the others.

Abstract The objective of this work is to evaluate the effect of fire on ant assemblages in savanna and forest typologies in the Reserva Natural da Serra do Tombador in Cavalcante - Goiás, Brazil. Ant pitfalls traps were installed and subdivided into Burnt Cerrado (BC), Unburnt Cerrado (UC), Burnt Forest (BF) and Unburnt Forest (UF), and the samples were sorted, assembled and identified. The constancy and abundance of individuals, and the frequency of distribution of the genera in the total area and by treatment were evaluated. The UF, BF, UC and BC had 19, 14, 8 and 15 genera, with Jackknife 1 index indicating 18.5, 24.4, 8.9 and 20.4 respectively. The Shannon diversity index for the genera was 0.8462, 0.7604, 0.6448 and 0.5992 for UF, BF, BC and UC respectively. The Cerrado showed greater abundance of individuals and greater ant diversity index in relation to Forest when in presence of fire.