Abstract:-The Paratudo (Tabebuia aurea) is a species occurring in the Pantanal of Miranda, Mato Grosso do Sul, Brazil, an area characterized by seasonal flooding. To evaluate the tolerance of this plant to flooding, plants aged four months were grown in flooded soil and in non-flooded soil (control group). Stomatal conductance, transpiration and CO 2 assimilation were measured during the stress (48 days) and recovery (11 days) period, totalling 59 days. The values of stomatal conductance of the control group and stress… Show more
“…In addition, changes in the photosynthetic apparatus and protection mechanisms associated with the activity of antioxidant enzymes also stand out [6] [7] [8] [9].…”
The Copaifera langsdorffii Desf. seedlings, popularly known as "copaiba" or diesel tree, present a natural occurrence in the riparian forests of the Brazilian Cerrado, however, not much is known about their capacity to recover from flooding, particularly when the focus is on their establishment and use in programs for the recovery of degraded areas near watercourses and subject to flooding. The objective of this study was to evaluate over time the recovery of the efficiency of the photosynthetic apparatus and the antioxidant activity of C. langsdorffii seedlings flooded during different periods. The pots with the seedlings were placed in a plastic tank and submerged with water, and were removed from the flood condition every 21 days (0, 21, 42, 63 and 84 days), and evaluated every 30 days (0, 30, 60, 90 and 120 days). The seedlings tolerated the flooding for up to 42 days, recovering after suspension of this condition. Seedlings flooded for 63 and 84 days showed lower recovery capacity after flooding, independently of the evaluation period. Under these conditions, lower efficiency of the photosynthetic apparatus, gas exchange, photo assimilate production and seedling quality were observed.
“…In addition, changes in the photosynthetic apparatus and protection mechanisms associated with the activity of antioxidant enzymes also stand out [6] [7] [8] [9].…”
The Copaifera langsdorffii Desf. seedlings, popularly known as "copaiba" or diesel tree, present a natural occurrence in the riparian forests of the Brazilian Cerrado, however, not much is known about their capacity to recover from flooding, particularly when the focus is on their establishment and use in programs for the recovery of degraded areas near watercourses and subject to flooding. The objective of this study was to evaluate over time the recovery of the efficiency of the photosynthetic apparatus and the antioxidant activity of C. langsdorffii seedlings flooded during different periods. The pots with the seedlings were placed in a plastic tank and submerged with water, and were removed from the flood condition every 21 days (0, 21, 42, 63 and 84 days), and evaluated every 30 days (0, 30, 60, 90 and 120 days). The seedlings tolerated the flooding for up to 42 days, recovering after suspension of this condition. Seedlings flooded for 63 and 84 days showed lower recovery capacity after flooding, independently of the evaluation period. Under these conditions, lower efficiency of the photosynthetic apparatus, gas exchange, photo assimilate production and seedling quality were observed.
“…Under these conditions, plant needs more energy for surviving the flood waters, resulting in a decrease of biosynthesis of secondary metabolites (Irfan et al 2010;Ferner et al 2012). This idea is supported by a recent study, where it was observed that plants of T. aurea subjected to flooding conditions reduce their physiological activities (Oliveira and Gualtieri 2016).…”
It is common in the Pantanal the occurrence of monodominant formations, such as "paratudal" dominated by Tabebuia aurea. Although it is of high importance, little is known about how it is maintained and what factors limit its progress. We investigated the variation of secondary metabolism between individuals located on the edge and center of the formation as well as the effect of flood pulse and what part of the plant (stem bark or leaves) is there greater accumulation of iridoids glycosides, and if is there a translocation of specioside between them. We collected stem bark and leaves samples from individuals of T. aurea located in the center and edge of paratudal in drought and flooded season, sampled individuals were the same in both seasons. We also analyzed the topographic profile of paratudal. Ours results showed that the specioside concentration in stem bark decreased during flood season only on the edge of paratudal and this region was lower than the center. Individuals located on the edge stay more time exposed to the flooding effect. These results suggest that the flooding is the main cause of the change in the specioside concentration on monodominant formation and the topography should delimitate the monoformation.
“…For example, stomatal closure is a commonly reported early response to soil flooding (Pezeshki 2001, Herrera et al 2008). This stomatal closure decreases CO 2 diffusion into the leaf (Farquhar and Sharkey 1982), leading to a decline in photosynthesis (Lavinsky et al 2007, Mielke and Schaffer 2011, Pimentel et al 2014, Oliveira and Gualtieri 2016, a decrease in photosynthate production, followed by a decline in biomass accumulation (Sena Gomes and Kozlowski 1980, Mielke et al 2003, Mielke and Schaffer 2010, Branco et al 2017.…”
We studied the impacts of light availability and soil flooding on biomass accumulation and tissue biomass fractions in Lindera melissifolia (Walt.) Blume, an endangered woody shrub of the southeastern United States. Our experiment was located in a large-scale flooding research facility where plants were established and grown for three years while receiving combinations of 70%, 37%, or 5% of full sunlight with either 0, 45, or 90 days of soil flooding. We hypothesized that biomass accumulation would decrease with decreasing light availability and that soil flooding would further reduce plant mass. In the absence of soil flooding, shrubs receiving 37% light accumulated the greatest biomass (972 g), shrubs receiving 70% light were intermediate in biomass accumulation (737 g), and shrubs receiving 5% light accumulated the least biomass (14 g). Shrubs raised beneath 37% light had root biomass fractions less indicative of water stress than shrubs raised beneath 70% light, and leaf and stem biomass fractions less indicative of light deprivation than shrubs raised beneath 5% light. The light environment also influenced how soil flooding affected L. melissifolia biomass accumulation. Soil flooding had no detectable effect on the amount of biomass accumulated by shrubs acclimated to 5% light. However, shrubs acclimated to 70% or 37% light showed a 26% decrease in biomass accumulation after 90 days of soil flooding. Our findings demonstrate a responsive plasticity of L. melissifolia biomass accumulation relative to light availability and soil flooding, and this plasticity was driven by shifts among leaf, stem, and root biomass fractions. This plasticity supports development of silvicultural options for active management of this endangered species in floodplain forests of the Mississippi Alluvial Valley.
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