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13 pages, 2187 KiB  
Article
Defense Mechanisms of Xylopia aromatica (Lam.) Mart. in the Dry Season in the Brazilian Savanna
by Felipe Campos, Maria Vieira, Marília Sousa, Letícia Jorge, Gisela Ferreira, Marcia Marques and Carmen Boaro
Life 2024, 14(11), 1416; https://doi.org/10.3390/life14111416 - 2 Nov 2024
Viewed by 554
Abstract
Water availability and light during the dry and rainy seasons in the Cerrado may influence plants’ stomatal movement and the entry of CO2 for organic synthesis, which is the main electron drain. A lower stomatal conductance may contribute to the energy accumulated [...] Read more.
Water availability and light during the dry and rainy seasons in the Cerrado may influence plants’ stomatal movement and the entry of CO2 for organic synthesis, which is the main electron drain. A lower stomatal conductance may contribute to the energy accumulated in the chloroplasts being directed towards the synthesis of compounds, which contributes to the activity of antioxidant enzymes to neutralize reactive oxygen species. Xylopia aromatica is a characteristic Cerrado species, and it is often recommended for recovering degraded areas. This study aimed to investigate the influence of the dry and rainy seasons on the metabolic adjustments of Xylopia aromatica in a portion of the Brazilian savanna in the state of São Paulo. In the rainy season, better photosynthetic performance led to greater investment in essential oil production. In the dry season, the plants may direct part of their reducing sugars to the syntheses of carotenoids and anthocyanins, which may help the antioxidant enzymes to neutralize reactive oxygen species. Carotenoids assist in the dissipation of photosystem energy, which has the potential to cause oxidative stress. During this season, lower stomatal conductance prevented excessive water loss. These results suggest the acclimatization of this species to the conditions of the Brazilian savanna. Full article
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<p>Relative humidity (RH, %) <span class="html-italic">p</span> ≤ 0.001, relative water content (RWC, %) <span class="html-italic">p</span> ≤ 0.001, and leaf vapor pressure deficit (VpdL, kPa) <span class="html-italic">p</span> ≤ 0.001 of <span class="html-italic">Xylopia aromatica</span> evaluated in the dry season (Dry1 and Dry2) and in the rainy season (Rainy1 and Rainy2) in the Brazilian savanna of Botucatu, SP, Brazil. Medium values. Capital letters test data through the years, lowercase letters test dry and rainy seasons. Means followed by the same letter did not differ from each other in the Tukey test at 5% probability.</p>
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<p>The efficiency of photosystem II (Fv′/Fm′) <span class="html-italic">p</span> &lt; 0.288, the fraction of light absorbed by PSII antenna that is dissipated as heat (<span class="html-italic">D</span>) <span class="html-italic">p</span> &lt; 0.288, effective quantum efficiency (ɸPSII) <span class="html-italic">p</span> ≤ 0.001, electron transport rate (ETR) <span class="html-italic">p</span> ≤ 0.001, and fraction of excitation energy not dissipated in the antenna that cannot be utilized for photochemistry (<span class="html-italic">Ex</span>) <span class="html-italic">p</span> &lt; 0.008 of <span class="html-italic">Xylopia aromatica</span> evaluated in the dry season (Dry1 and Dry2) and in the rainy season (Rainy1 and Rainy2) in the Brazilian savanna of Botucatu, SP, Brazil. Medium values. Capital letters test data through the years, lowercase letters test dry and rainy seasons. Means followed by the same letter did not differ from each other in the Tukey test at 5% probability.</p>
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<p>Leaf CO<sub>2</sub> assimilation rate (<span class="html-italic">Anet</span>, μmol m<sup>−2</sup> s<sup>−1</sup>) <span class="html-italic">p</span> ≤ 0.001, accumulation in the substomatal chamber (<span class="html-italic">Ci</span>, μmol CO<sub>2</sub> mol Pa<sup>−1</sup>) <span class="html-italic">p</span> ≤ 0.001, stomatal conductance (<span class="html-italic">gs</span>, mmol m<sup>−2</sup> s<sup>−1</sup>) <span class="html-italic">p</span> ≤ 0.001, transpiration rate (E, mmol m<sup>−2</sup> s<sup>−1</sup>) <span class="html-italic">p</span> &lt; 0.002, carboxylation efficiency (<span class="html-italic">Anet</span>/<span class="html-italic">Ci</span>, μmol m<sup>−2</sup> s<sup>−1</sup> Pa<sup>−1</sup>) <span class="html-italic">p</span> ≤ 0.001, and instantaneous water-use efficiency (iWUE, μmol CO<sub>2</sub> (mmol H<sub>2</sub>O<sup>−1</sup>) <span class="html-italic">p</span> &lt; 0.005 of <span class="html-italic">Xylopia aromatica</span> evaluated in the dry season (Dry1 and Dry2) and in the rainy season (Rainy1 and Rainy2) in the Brazilian savanna of Botucatu, SP, Brazil. Medium values. Capital letters test data through the years, lowercase letters test dry and rainy seasons. Means followed by the same letter did not differ from each other in the Tukey test at 5% probability.</p>
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<p>α-pinene (<span class="html-italic">p</span> &lt; 0.043) and β-pinene (<span class="html-italic">p</span> &lt; 0.030); spathulenol: season (<span class="html-italic">p</span> ≤ 0.001), year (<span class="html-italic">p</span> ≤ 0.001); bicyclogermacrene: season (<span class="html-italic">p</span> ≤ 0.001), year (<span class="html-italic">p</span> ≤ 0.001); β-phellandrene (<span class="html-italic">p</span> &lt; 0.012), and essential oil yield of <span class="html-italic">Xylopia aromatica</span> evaluated in the dry season (Dry1 and Dry2) and in the rainy season (Rainy1 and Rainy2) in the Brazilian savanna of Botucatu, SP, Brazil. Medium values. Capital letters test data through the years, lowercase letters test dry and rainy seasons. Means followed by the same letter did not differ from each other in the Tukey test at 5% probability.</p>
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13 pages, 3639 KiB  
Article
Savanna Plants Have a Lower Hydraulic Efficiency than Co-Occurring Species in a Rainforest
by Xiaorong Peng, Da Yang, Qin Wang, Yu Tian, Ke Yan, Yunbing Zhang, Shijian Yang and Jiaolin Zhang
Forests 2024, 15(11), 1912; https://doi.org/10.3390/f15111912 - 30 Oct 2024
Viewed by 437
Abstract
A plant species can have diverse hydraulic strategies to adapt to different environments. However, the water transport divergence of co-occurring species in contrasting habitats remains poorly studied but is important for understanding their ecophysiology adaptation to their environments. Here, we investigated whole-branch, stem [...] Read more.
A plant species can have diverse hydraulic strategies to adapt to different environments. However, the water transport divergence of co-occurring species in contrasting habitats remains poorly studied but is important for understanding their ecophysiology adaptation to their environments. Here, we investigated whole-branch, stem and leaf water transport strategies and associated morphology traits of 11 co-occurring plant species in Yuanjiang valley-type savanna (YJ) with dry–hot habitats and Xishuangbanna tropical seasonal rainforest (XSBN) with wet–hot habits and tested the hypothesis that plants in YJ have a lower water transport efficiency than co-occurring species in XSBN. We found high variation in whole-branch, stem and leaf hydraulic conductance (Kshoot; Kstem and Kleaf) between YJ and XSBN, and that Kstem was significantly higher than Kleaf in these two sites (Kstem/Kleaf: 16.77 in YJ and 6.72 in XSBN). These plants in YJ with significantly lower Kshoot and Kleaf but higher sapwood density (WD) and leaf mass per area (LMA) showed a lower water transport efficiency regarding less water loss and the adaptation to the dry–hot habitat compared to co-occurring species in XSBN. In contrast, these co-occurring plants in XSBN with higher Kshoot and Kleaf but lower WD and LMA tended to maximize water transport efficiency and thus growth potential in the wet–hot habitat. Our findings suggest that these co-occurring species employ divergent hydraulic efficiency across YJ and XSBN so that they can benefit from the contrasting hydraulic strategies in adaptation to their respective habitats. Full article
(This article belongs to the Section Forest Ecophysiology and Biology)
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<p>Comparisons of stem hydraulic conductance (<span class="html-italic">K</span><sub>stem</sub>, ×10<sup>−4</sup> kg s<sup>−1</sup> MPa<sup>−1</sup> m<sup>−2</sup>) and leaf hydraulic conductance (<span class="html-italic">K</span><sub>leaf</sub>, ×10<sup>−4</sup> kg s<sup>−1</sup> MPa<sup>−1</sup> m<sup>−2</sup>) in these two sites: YJ and XSBN. **: <span class="html-italic">p</span> &lt; 0.01.</p>
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<p>The log–log relationships of (<b>a</b>) leaf hydraulic conductance (<span class="html-italic">K</span><sub>leaf</sub>) with stem hydraulic conductance (<span class="html-italic">K</span><sub>stem</sub>), (<b>b</b>) leaf hydraulic conductance (<span class="html-italic">K</span><sub>leaf</sub>) with whole-branch hydraulic conductance (<span class="html-italic">K</span><sub>shoot</sub>), (<b>c</b>) stem hydraulic conductance (<span class="html-italic">K</span><sub>stem</sub>) with whole-branch hydraulic conductance (<span class="html-italic">K</span><sub>shoot</sub>) across the XSBN (blue circle) and the YJ (red triangle). The absence of lines indicates the correlation is not significant (<span class="html-italic">p</span> &gt; 0.05).</p>
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<p>The log–log relationships between sapwood density (WD) and (<b>a</b>) whole-branch hydraulic conductance (<span class="html-italic">K</span><sub>shoot</sub>), (<b>b</b>) stem hydraulic conductance (<span class="html-italic">K</span><sub>stem</sub>), (<b>c</b>) leaf hydraulic conductance (<span class="html-italic">K</span><sub>leaf</sub>), and (<b>d</b>) ratio of stem to leaf hydraulic conductance (<span class="html-italic">K</span><sub>stem</sub>/<span class="html-italic">K</span><sub>leaf</sub>) in these two sites (YJ: red triangle; XSBN: blue circle). Lines depict parameters of linear regressions, and shaded areas represent 95% confidence intervals. The absence of lines indicates the correlation is not significant (<span class="html-italic">p</span> &gt; 0.05).</p>
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<p>The log–log relationship between sapwood density (WD) and leaf mass per area (LMA) in these two sites (YJ: red triangle; XSBN: blue circle). Lines depict parameters of linear regressions, and shaded areas represent 95% confidence intervals. The absence of lines indicates the correlation is not significant (<span class="html-italic">p</span> &gt; 0.05).</p>
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<p>Principal component analysis (PCA) using log-transformed data for 8 traits of 11 co-occurring species between these two sites (YJ: red triangle; XSBN: blue circle). Whole-branch hydraulic conductance (<span class="html-italic">K</span><sub>shoot</sub>), stem hydraulic conductance (<span class="html-italic">K</span><sub>stem</sub>), leaf hydraulic conductance (<span class="html-italic">K</span><sub>leaf</sub>), ratio of stem to leaf hydraulic conductance (<span class="html-italic">K</span><sub>stem</sub>/<span class="html-italic">K</span><sub>leaf</sub>), sapwood density (WD), leaf mass per area (LMA), ratio of petiole mass to lamina mass (PM/LM), petiole mass (PM).</p>
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23 pages, 16662 KiB  
Article
Evaluating Burn Severity and Post-Fire Woody Vegetation Regrowth in the Kalahari Using UAV Imagery and Random Forest Algorithms
by Madeleine Gillespie, Gregory S. Okin, Thoralf Meyer and Francisco Ochoa
Remote Sens. 2024, 16(21), 3943; https://doi.org/10.3390/rs16213943 - 23 Oct 2024
Viewed by 601
Abstract
Accurate burn severity mapping is essential for understanding the impacts of wildfires on vegetation dynamics in arid savannas. The frequent wildfires in these biomes often cause topkill, where the vegetation experiences above-ground combustion but the below-ground root structures survive, allowing for subsequent regrowth [...] Read more.
Accurate burn severity mapping is essential for understanding the impacts of wildfires on vegetation dynamics in arid savannas. The frequent wildfires in these biomes often cause topkill, where the vegetation experiences above-ground combustion but the below-ground root structures survive, allowing for subsequent regrowth post-burn. Investigating post-fire regrowth is crucial for maintaining ecological balance, elucidating fire regimes, and enhancing the knowledge base of land managers regarding vegetation response. This study examined the relationship between bush burn severity and woody vegetation post-burn coppicing/regeneration events in the Kalahari Desert of Botswana. Utilizing UAV-derived RGB imagery combined with a Random Forest (RF) classification algorithm, we aimed to enhance the precision of burn severity mapping at a fine spatial resolution. Our research focused on a 1 km2 plot within the Modisa Wildlife Reserve, extensively burnt by the Kgalagadi Transfrontier Fire of 2021. The UAV imagery, captured at various intervals post-burn, provided detailed orthomosaics and canopy height models, facilitating precise land cover classification and burn severity assessment. The RF model achieved an overall accuracy of 79.71% and effectively identified key burn severity indicators, including green vegetation, charred grass, and ash deposits. Our analysis revealed a >50% probability of woody vegetation regrowth in high-severity burn areas six months post-burn, highlighting the resilience of these ecosystems. This study demonstrates the efficacy of low-cost UAV photogrammetry for fine-scale burn severity assessment and provides valuable insights into post-fire vegetation recovery, thereby aiding land management and conservation efforts in savannas. Full article
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<p>Kgalagadi Transfrontier Fire (KTF) extent and location in Botswana. Modisa is indicated by a red star in the left panel of the figure. The natural color satellite imagery of the Kgalagadi Transfrontier Fire in the left panel was acquired by the National Aeronautics and Space Administration’s (NASA, Washington, DC, USA) Moderate Resolution Imaging Spectroradiometer (MODIS, Washinton, DC, USA) from its Aqua satellite on 8 September 2021 at a 250-m resolution.</p>
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<p>The top left corner depicts the 1 sq. km post-burn plot of land that this study primarily focused on. The bottom panel offers a closer look at the burn impacts within the plot of land. The top right corner displays the location of the study site in Botswana, Modisa and is indicated by a red star.</p>
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<p>Flow chart showing the steps of the burn severity classification model along with the datasets and software used. R: red; G: green; B: blue; GLCM: gray-level co-occurrence matrix; UAS: unmanned aerial system.</p>
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<p>Visualizations of land cover classification schema and their corresponding burn severity rankings.</p>
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<p>Original RGB drone images (<b>left</b>) and the manually classified land cover classifications (<b>right</b>).</p>
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<p>Visual comparison of 12-h post-burn imagery and 6-month post-burn imagery. Woody vegetation regrowth visualization is defined and compared to herbaceous cover, as indicated by the red box outlines. Regrowth was determined based on patch regrowth rather than analysis at the pixel level.</p>
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<p><b>Top Panel</b>: Original drone image 12 h post burn (<b>left</b>) and the Random Forest model-predicted land cover classification map (<b>right</b>). Three outlined regions (A, B, C) are indicated. <b>Bottom Panels</b>: The zoomed-in regions from the model-predicted map and the original RGB map for better visualization.</p>
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<p>Random Forest classification results reclassified to represent burn severity rankings.</p>
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<p>Confusion matrix for Random Forest classification of burn severity. Each cell shows the proportion of observations predicted versus the actual observed categories, highlighting the model’s precision and misclassification rates. Numerical values and gradient color of the cells represent the normalized value of correct pixel predictions.</p>
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<p>Feature importance within the Random Forest classification model. CHM = Canopy Height Model; RGB = Red band, green band, blue band; GCC = Green Chromatic Coordinate; CI = Char Index; max_diff = Max Difference Index; EGI = Excessive Greenness Index; BI = Brightness Index.</p>
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<p>Woody vegetation survival and regrowth. This figure presents the probability of survival and regrowth in woody vegetation at 6 months and 2.5 years post-burn across the 1000 derived Monte Carlo outputs. Mean probabilities and standard deviations are calculated for each category. Wider violin plots indicate a higher likelihood of regrowth, while narrower plots suggest a lower likelihood.</p>
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<p>Sample of RGB images used within the manual classification dataset and their corresponding CHM in meters. White spots within the CHM are indicative of taller vegetation.</p>
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19 pages, 265 KiB  
Article
Community-Engaged Approaches for Improving the Inclusion of Diverse Communities in a Nutrition Clinical Trial
by Mopelola A. Adeyemo, Jessica Trinh, Darian Perez, Estabon Bozeman, Ejiro Ntekume, Jachael Gardner, Gail Thames, Tiffany Luong, Savanna L. Carson, Stefanie Vassar, Keith Norris, Zhaoping Li, Arleen F. Brown and Alejandra Casillas
Nutrients 2024, 16(21), 3592; https://doi.org/10.3390/nu16213592 - 23 Oct 2024
Viewed by 713
Abstract
Background: Cardiometabolic disease (CMD) disproportionately affects African American/Black (AA) and Latino communities. CMD disparities are exacerbated by their underrepresentation in clinical trials for CMD treatments including nutritional interventions. The study aimed to (1) form a precision nutrition community consultant panel (PNCCP) representative of [...] Read more.
Background: Cardiometabolic disease (CMD) disproportionately affects African American/Black (AA) and Latino communities. CMD disparities are exacerbated by their underrepresentation in clinical trials for CMD treatments including nutritional interventions. The study aimed to (1) form a precision nutrition community consultant panel (PNCCP) representative of Latino and AA communities in Los Angeles to identify barriers and facilitators to recruitment and retention of diverse communities into nutrition clinical trials and (2) develop culturally informed strategies to improve trial diversity. Methods: A deliberative community engagement approach was used to form a PNCCP for the Nutrition for Precision Health (NPH) trial, part of the of the All of Us research initiative. The PNCCP included individuals that provide services for Latino and AA communities who met during 11 virtual sessions over 1 year. Discussion topics included enhancing recruitment and cultural acceptance of the NPH trial. We summarized CCP recommendations by theme using an inductive qualitative approach. Results: The PNCCP included 17 adults (35% AA, 47% Latino). Four thematic recommendations emerged: reducing structural barriers to recruitment, the need for recruitment materials to be culturally tailored and participant-centered, community-engaged trial recruitment, and making nutrition trial procedures inclusive and acceptable. We outlined the study response to feedback, including the constraints that limited implementation of suggestions. Conclusion: This study centers community voices regarding the recruitment and retention of AA and Latino communities into a nutrition clinical trial. It highlights the importance of community engagement early on in protocol development and maintaining flexibility to enhance inclusion of diverse communities in nutrition clinical trials. Full article
(This article belongs to the Special Issue Dietary Interventions to Advance Equity in Cardiometabolic Health)
24 pages, 5753 KiB  
Article
Phenological Monitoring of Irrigated Sugarcane Using Google Earth Engine, Time Series, and TIMESAT in the Brazilian Semi-Arid
by Diego Rosyur Castro Manrique, Pabrício Marcos Oliveira Lopes, Cristina Rodrigues Nascimento, Eberson Pessoa Ribeiro and Anderson Santos da Silva
AgriEngineering 2024, 6(4), 3799-3822; https://doi.org/10.3390/agriengineering6040217 - 18 Oct 2024
Viewed by 620
Abstract
Monitoring sugarcane phenology is essential since the globalized market requires reliable information on the quantity of raw materials for the industrial production of sugar and alcohol. In this context, the general objective of this study was to evaluate the phenological seasonality of the [...] Read more.
Monitoring sugarcane phenology is essential since the globalized market requires reliable information on the quantity of raw materials for the industrial production of sugar and alcohol. In this context, the general objective of this study was to evaluate the phenological seasonality of the sugarcane varieties SP 79-1011 and VAP 90-212 observed from the NDVI time series over 19 years (2001–2020) from global databases. In addition, this research had the following specific objectives: (i) to estimate phenological parameters (Start of Season (SOS), End of Season (EOS), Length of Season (LOS), and Peak of Season (POS)) using TIMESAT software in version 3.3 applied to the NDVI time series over 19 years; (ii) to characterize the land use and land cover obtained from the MapBiomas project; (iii) to analyze rainfall variability; and (iv) to validate the sugarcane harvest date (SP 79-1011). This study was carried out in sugarcane growing areas in Juazeiro, Bahia, Brazil. The results showed that the NDVI time series did not follow the rainfall in the region. The sugarcane areas advanced over the savanna formation (Caatinga), reducing them to remnants along the irrigation channels. The comparison of the observed harvest dates of the SP 79-1011 variety to the values estimated with the TIMESAT software showed an excellent fit of 0.99. The mean absolute error in estimating the sugarcane harvest date was approximately ten days, with a performance index of 0.99 and a correlation coefficient of 0.99, significant at a 5% confidence level. The TIMESAT software was able to estimate the phenological parameters of sugarcane using MODIS sensor images processed on the Google Earth Engine platform during the evaluated period (2001 to 2020). Full article
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<p>Map of the sugarcane with the physical boundaries in RGB (red, green and blue) color composite Landsat-8 and the location under study.</p>
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<p>Graphical abstract steps for obtaining the phenological metrics. where: SOS = Start of Season, EOS = End Of Season, LOS = Length of the Season and POS = Peak of Season. Source: Adapted of Rodigheri et al. [<a href="#B40-agriengineering-06-00217" class="html-bibr">40</a>].</p>
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<p>TIMESAT software modules for processing NDVI time series in the TIMESAT software module.</p>
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<p>Application of the Savitsky–Golay filter (red curve) for a time series of NDVI scaled (black curve) as a function of time (days) to estimate phenological parameters: points (a) and (b) mark, respectively, start and end of the season, points (c) and (d) give the 80% levels, (e) displays the point with the maximum value, (f) displays the seasonal amplitude, (g) the seasonal length, and (h) and (i) are integrals showing the cumulative effect of vegetation during the season. Source: Jönsson and Eklundh [<a href="#B48-agriengineering-06-00217" class="html-bibr">48</a>].</p>
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<p>Meteorological data from the Meteorology Laboratory (LabMet) automatic weather station for the period 2008 to 2012, Juazeiro, Bahia, Brazil.</p>
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<p>Classification of the land use and land cover of the watershed using MapBiomas in its Collection 6 (2006–2012).</p>
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<p>Temporal distribution of the area cultivated with sugarcane in the watershed from 2001 to 2020 in Juazeiro, Bahia, Brazil.</p>
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<p>MODIS NDVI (2001–2020) for the total area and rainfall of Labmet Juazeiro (2008–2020) time series.</p>
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<p>NDVI time series and Savitsky–Golay filter for the sugarcane total area. The dots represent the start (in blue) and the end (in yellow) of the sugarcane phenological cycles.</p>
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<p>Sugarcane agricultural calendar in the test area from the SP 79-1011 and VAP 90-212. In blue, months referring to the phenological phases of sugarcane.</p>
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<p>Comparison of variety SP 79-1011 harvest dates observed with estimated values with TIMESAT software for the test area between 2006 to 2012.</p>
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19 pages, 3372 KiB  
Article
Remote Sensing and Field Data Analysis to Evaluate the Impact of Stone Bunds on Rainfed Agriculture in West Africa
by Meron Lakew Tefera, Hassan Awada, Mario Pirastru, James Mantent Kombiok, Joseph Adjebeng-Danquah, Ramson Adombilla, Peter Anabire Asungre, George Mahama, Alberto Carletti and Giovanna Seddaiu
Land 2024, 13(10), 1654; https://doi.org/10.3390/land13101654 - 10 Oct 2024
Viewed by 740
Abstract
This study evaluates the effectiveness of stone bunds in enhancing soil moisture, vegetation health, and crop yields in Ghana’s semi-arid Upper East Region, an important area for agricultural productivity in West Africa. In this region, agricultural practices are heavily impacted by erratic rainfall [...] Read more.
This study evaluates the effectiveness of stone bunds in enhancing soil moisture, vegetation health, and crop yields in Ghana’s semi-arid Upper East Region, an important area for agricultural productivity in West Africa. In this region, agricultural practices are heavily impacted by erratic rainfall and poor soil moisture retention, threatening food security. Despite the known benefits of traditional soil conservation practices like stone bunds, their effectiveness in this context has not been fully quantified. Field and remote sensing data were used to evaluate the influence of stone bunds on soil moisture dynamics, vegetation growth, and crop yield. Experimental plots with and without stone bunds were monitored for climate, soil water infiltration, and soil moisture and analyzed using the NDVI from Sentinel-2 satellite imagery over two growing seasons under sorghum production (2022–2023). The results indicated that stone bunds enhanced soil moisture retention and increased infiltration rates. The NDVI analysis consistently revealed higher vegetation health and growth in the plots with stone bunds, particularly during critical growth periods. The intermediate results of the conducted experiment indicated that stone bunds increased sorghum yields by over 35% compared to the control plots. The substantial agronomic benefits of stone bunds as a soil and water conservation strategy were evident, improving soil water infiltration, water retention, vegetation health, and crop yields. The findings support the broader adoption of stone bunds in semi-arid regions to enhance agricultural productivity and resilience against climate variability. Further research is recommended to explore the long-term impacts and the integration of stone bunds with other sustainable farming practices to optimize rainfed agricultural outcomes. Full article
(This article belongs to the Section Land Systems and Global Change)
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<p>Location of the experimental site in the Upper East Region, Nabdam District (<b>a</b>), specifically in Nangodi (Soliga) (<b>c</b>), Ghana (<b>b</b>).</p>
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<p>Graphical overview of stone bunds installed in the study area: dimensions and moisture sensor placement (MSP).</p>
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<p>Rainfall and temperature variability: 2022 and 2023 rainy seasons in the study area (Nabdam).</p>
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<p>Sample stone bund polygon for NDVI data extraction in the study area (Nabdam, Ghana): Google Earth (<b>a</b>), actual image (<b>b</b>), and Sentinel 2 retrieved NDVI pixels for the 4 September 2023 (<b>c</b>).</p>
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<p>Observed time series of the rainfall and the soil water contents in the stone bunds and control areas at (<b>a</b>) 10 cm of soil depth; (<b>b</b>) 20 cm of soil depth. Data interval is 15 min.</p>
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<p>Cumulative infiltration (F(t)) and infiltration rate (f(t)) were measured in April 2022. The black lines (f(t)) represent the infiltration rates, whereas the brown lines (F(t)) illustrate the cumulative infiltration accumulated over time.</p>
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<p>Temporal dynamics of mean daily normalized difference vegetation index (NDVI) values for two consecutive years across different agricultural stages, marked by days of the year (DOY). The shaded regions denote the confidence intervals, providing an estimate of variability around the mean and the vertical dashed line separates the cropping season (Sowing, Mid-season and Harvesting periods).</p>
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<p>NDVI pixel distribution over the two seasons (2022–2023).</p>
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<p>Mean yield of sorghum (Kapaala White) under stone bunds and control plot over the two years.</p>
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18 pages, 7073 KiB  
Article
Species Substitution and Changes in the Structure, Volume, and Biomass of Forest in a Savanna
by Kennedy Nunes Oliveira, Eder Pereira Miguel, Matheus Santos Martins, Alba Valéria Rezende, Juscelina Arcanjo dos Santos, Mauro Eloi Nappo and Eraldo Aparecido Trondoli Matricardi
Plants 2024, 13(19), 2826; https://doi.org/10.3390/plants13192826 - 9 Oct 2024
Viewed by 679
Abstract
Research related to Cerradão vegetation focuses more on the floristic-structural aspect, with rare studies on the quantification of volume and biomass stocks, and even fewer investigating the increments of these attributes. Using a systematic sampling method with subdivided strips and 400 m2 [...] Read more.
Research related to Cerradão vegetation focuses more on the floristic-structural aspect, with rare studies on the quantification of volume and biomass stocks, and even fewer investigating the increments of these attributes. Using a systematic sampling method with subdivided strips and 400 m2 plots, the density found was 1135, 1165, and 1229 trees/ha in 2012, 2020, and 2023, respectively, in Lajeado State Park, Tocantins State, Brazil. Volume was estimated using the equation v=0.000085D2.122270H0.666217, and biomass was estimated using the equation AGB=0.0673ρD2H0.976. Vegetation dynamics were assessed using growth increment, recruitment, mortality, turnover rate, and time. The results indicated that dynamics have increased since the start of monitoring. Typical Cerrado species, in the strict sense, were replaced by those from forest environments. The total production in volume and biomass was 160.91 m3/ha and 118.10 Mg/ha, respectively, in 2023. The species of Emmotum nitens, Mezilaurus itauba, Ocotea canaliculata, and Sacoglottis guianensis showed the highest increment values in volume and biomass. For the community, the average values were 4.04 m3/ha/year and 3.54 Mg/ha/year. The community has not yet reached its carrying capacity and stores a significant amount of biomass. This is influenced by the transition of the study area from an exploited environment to a conservation unit (park) and by its location in a transitional area with the Amazon biome. Full article
(This article belongs to the Collection Forest Environment and Ecology)
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<p>Importance Value (IV%), volume (V), and aboveground biomass (AGB) of the top 10 species according to IV% for the years of 2012, 2020, and 2023 in the Cerradão of Lajeado State Park, Tocantins, Brazil. FR is relative frequency; DoR is relative dominance; and DR is relative density.</p>
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<p>Accumulation curve of richness and diversity as a function of the number of sampling units in the Cerradão of Lajeado State Park, Tocantins, Brazil. Guides = 0 and 1, where guides refer to the Hill number “q” (0 = species richness and 1 = Shannon–Wiener diversity) [<a href="#B32-plants-13-02826" class="html-bibr">32</a>]. Rarefaction (solid line) and extrapolation (dashed lines) correspond to mean values and standard deviation ranges with confidence intervals (α = 0.05).</p>
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<p>Distribution of the frequency of individuals (N) in the arboreal community of the Cerradão located in Lajeado State Park, Tocantins, Brazil.</p>
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<p>Volume and aboveground biomass production of the arboreal vegetation in Cerradão over time in Lajeado State Park, Tocantins, Brazil.</p>
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<p>Changes in the woody community by diameter class of the Cerradão in Lajeado State Park, Tocantins, Brazil. N is the number of trees; V is volume; and AGB is the aboveground biomass.</p>
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<p>Volume (V) and aboveground biomass (AGB) of the woody vegetation in the Cerradão of Lajeado State Park, as a function of height class.</p>
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<p>The distribution of sampling units (50) and the location of the study area in the Cerradão of Lajeado State Park, Tocantins State, Brazil.</p>
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<p>(<b>a</b>) Stakes for demarcat ion of sampling units; (<b>b</b>) Use of caliper for diameter measurements; (<b>c</b>) Graduated pole for height measurement and estimation; and (<b>d</b>) Collection of botanical material for subsequent identification and herbarium preparation.</p>
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13 pages, 4087 KiB  
Article
Molecular Phylogenetics and Historical Biogeography of Subtribe Ecliptinae (Asteraceae, Heliantheae)
by Rafael Felipe de Almeida, Maria Alves, Cássio van den Berg, Marco O. O. Pellegrini, Morgan R. Gostel and Nádia Roque
Plants 2024, 13(19), 2817; https://doi.org/10.3390/plants13192817 - 8 Oct 2024
Viewed by 955
Abstract
We present a molecular phylogeny for the subtribe Ecliptinae (Asteraceae, Heliantheae) based on three plastid (matK, psbA-trnH, and trnQ-rps16) and two nuclear (nrITS and nrETS) markers. The results of the phylogenetic reconstruction were utilised as a topological constraint for [...] Read more.
We present a molecular phylogeny for the subtribe Ecliptinae (Asteraceae, Heliantheae) based on three plastid (matK, psbA-trnH, and trnQ-rps16) and two nuclear (nrITS and nrETS) markers. The results of the phylogenetic reconstruction were utilised as a topological constraint for a subsequent divergence dating analysis and ancestral range reconstructions. We sampled 41 species and 40 genera (72%) of Ecliptinae and two species of Montanoa (as outgroups) to elucidate the generic relationships between the genera of this subtribe. The Bayesian inference (BI) and Maximum Likelihood (ML) analyses were performed for the combined molecular dataset. The divergence dating analysis was performed using a relaxed, uncorrelated molecular clock with BEAST v1.8.4 and calibrated using a single secondary calibration point from a recently published chronogram for the family. The ancestral range reconstructions focusing on continents (i.e., South America, North America, Africa, Asia, and Oceania) and biomes (Dry forests, Altitudinal grasslands, Savannas, and Rainforests) were performed on BioGeoBEARS. Our phylogenetic results indicate that the genera of Ecliptinae are grouped into five clades, informally named the Monactis, Oblivia, Blainvillea, Wedelia, and Melanthera clades. The most recent, common ancestor of Ecliptinae was widespread in the North and South American dry forests at 8.16 Ma and mainly radiated in these regions up to the Pleistocene. At least eight dispersal events to South America and four dispersal events from North America to Africa, Asia, and Oceania took place during this period in all five informal clades of Ecliptinae. At least 13 biome shifts from dry forests to rainforests were evidenced, in addition to ten biome shifts from dry forests to altitudinal grasslands and savannas. These results corroborate the mid-late Miocene to early Pleistocene radiation of Ecliptinae in tropical dry forests. Future studies should aim to sample the remaining 14 unsampled genera of Ecliptinae to position them in one of the five informal clades proposed in this study. Full article
(This article belongs to the Section Plant Systematics, Taxonomy, Nomenclature and Classification)
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<p>Molecular phylogeny of Ecliptinae, highlighting the five informal clades proposed here: right tree shows posterior probabilities of the Bayesian inference shown above branches and bootstrap values shown below branches, and left tree shows branch lengths. (<b>A</b>). <span class="html-italic">Melanthera nivea</span> (L.) Small by Katie Z, (<b>B</b>). <span class="html-italic">Wedelia calycina</span> Rich. by Juan Gabriel, (<b>C</b>). <span class="html-italic">Eclipta prostrata</span> (L.) by Nana Ten, (<b>D</b>). <span class="html-italic">Blainvillea gayana</span> Cass. by Frederico Acaz Sonntag, (<b>E</b>). <span class="html-italic">Otopappus verbesinoides</span> Benth. by Luis Humberto Vicente-Rivera, and (<b>F</b>). <span class="html-italic">Kingianthus paniculatus</span> (Turcz.) H.Rob. by Yanna Paola.</p>
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<p>Character-mapping of 23 morphological traits in Ecliptinae, highlighting the five informal clades proposed here. Red circles represent apomorphies. Transparent circles represent homoplasies. Numbers above circles represent character numbers, and numbers below circles represent character states.</p>
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<p>Chronogram of Ecliptinae showing mean node ages estimated for branches. Blue bars represent 95% Highest Posterior Densities (HPD) for the estimated median dates.</p>
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<p>Continental ancestral range reconstruction for Ecliptinae: (<b>A</b>) South America, (<b>B</b>) North America, (<b>C</b>) Africa, (<b>D</b>) Asia, and (<b>E</b>) Oceania.</p>
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<p>Biome ancestral range reconstruction for Ecliptinae: (<b>A</b>) Dry forests, (<b>B</b>) Altitudinal grasslands, (<b>C</b>) Savannas, and (<b>D</b>) Rainforests.</p>
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12 pages, 1367 KiB  
Article
Canopy Characteristics of Gamba Grass Cultivars and Their Effects on the Weight Gain of Beef Cattle under Grazing
by Gustavo José Braga, Allan Kardec Braga Ramos, Marcelo Ayres Carvalho, Carlos Eduardo Lazarini Fonseca and Claudio Takao Karia
Agronomy 2024, 14(10), 2293; https://doi.org/10.3390/agronomy14102293 - 6 Oct 2024
Viewed by 521
Abstract
Gamba grass (Andropogon gayanus Kunth) is a tussock-forming forage species adapted to acid soils of Brazilian savannas and cultivated for grazing pastures. Four decades since its release, Planaltina prevails as the most commercialized cultivar of the species, even though the new cultivar [...] Read more.
Gamba grass (Andropogon gayanus Kunth) is a tussock-forming forage species adapted to acid soils of Brazilian savannas and cultivated for grazing pastures. Four decades since its release, Planaltina prevails as the most commercialized cultivar of the species, even though the new cultivar BRS Sarandi could be a better alternative for Gamba-grass-based farms by presenting a greater leaf:stem ratio. The objective of this study was to evaluate the average daily live weight gain (ADG) of Nellore bulls (Bos indicus) for two Gamba grass cultivars—Planaltina and Sarandi. The experiment was conducted in Planaltina, Federal District, Brazil, for 3 years, namely 2018, 2018–2019, and 2020. The experimental design was a completely randomized block design with two treatments and three replicates, each one continuously stocked at three stocking rates (SR)—1.3, 2.6, and 4 young bulls/ha. Canopy height (CH), forage mass (FM), plant-part proportion (green leaf, stem, and dead material), and nutritive value were evaluated. In 2018, mean ADG for Sarandi pastures was greater (0.690 kg/bull/d) than that of Planaltina (0.490 kg/bull/d) (p < 0.10). In the subsequent year (2018–2019), there was no effect of cultivar (p > 0.10), while in 2020 the ADG was again affected by cultivar (p < 0.10), confirming the advantage of Sarandi (0.790 kg/bull/d) over Planaltina (0.650 kg/bull/d). In 2018 and 2020, the percentage of stems for Sarandi was about 3–6 pp less than for Planaltina (p < 0.10). As well as for stems, Sarandi pastures presented a shorter CH in 2028 and 2020 (6–7%) (p < 0.10). The positive high correlation of leaf:stem ratio with ADG (r = 0.70) probably predisposed the superiority of Sarandi over Planaltina. The distinguishing plant-part composition of Sarandi canopy promotes increasing weight gain of beef cattle when compared to cv. Planaltina. Full article
(This article belongs to the Special Issue Advances in Grassland Productivity and Sustainability — 2nd Edition)
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<p>Scatter plots of forage mass (FM, kg MS/ha); canopy height (CH, cm); leaf (%); stem (%); dead material (%); leaf:stem ratio; leaf bulk density (kg MS/ha/cm); leaf allowance (LA, kg MS of leaves/kg live weight); crude protein (CP, g/kg); in vitro dry matter digestibility (IVDMD, g/kg); neutral detergent fiber (NDF, g/kg); and acid detergent fiber (ADF, g/kg) with average daily gain (ADG, kg/bull/d) of Nellore bulls in pastures of <span class="html-italic">Andropogon gayanus</span> Kunth cv. Sarandi (SAR) and cv. Planaltina (PLA), Planaltina, FD, Brazil. Each point represents the mean value of each experimental unit (paddock).</p>
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<p>Average daily live weight gain (ADG, kg/bull/d) of Nellore bulls in <span class="html-italic">Andropogon gayanus</span> Kunth pastures of cv. Sarandi (SAR) and cv. Planaltina (PLA) for low, medium, and high stocking rates (SRs) during three years (2018, 2018–2019, and 2020). Bars represent ± standard error of the mean (s.e.).</p>
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<p>Leaf:stem ratio of <span class="html-italic">Andropogon gayanus</span> Kunth cv. Sarandi (SAR) and cv. Planaltina (PLA) for low, medium, and high stocking rates (SRs) during three years (2018, 2018–2019, and 2020). Bars represent ± standard error of the mean (s.e.).</p>
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14 pages, 3976 KiB  
Article
Generic and Specific Models for Volume Estimation in Forest and Savanna Phytophysiognomies in Brazilian Cerrado
by Yanara Ferreira de Souza, Eder Pereira Miguel, Adriano José Nogueira Lima, Álvaro Nogueira de Souza, Eraldo Aparecido Trondoli Matricardi, Alba Valéria Rezende, Joberto Veloso de Freitas, Hallefy Junio de Souza, Kennedy Nunes Oliveira, Maria de Fátima de Brito Lima and Leonardo Job Biali
Plants 2024, 13(19), 2769; https://doi.org/10.3390/plants13192769 - 3 Oct 2024
Viewed by 753
Abstract
The Cerrado has high plant and vertebrate diversity and is an important biome for conserving species and provisioning ecosystem services. Volume equations in this biome are scarce because of their size and physiognomic diversity. This study was conducted to develop specific volumetric models [...] Read more.
The Cerrado has high plant and vertebrate diversity and is an important biome for conserving species and provisioning ecosystem services. Volume equations in this biome are scarce because of their size and physiognomic diversity. This study was conducted to develop specific volumetric models for the phytophysiognomies Gallery Forest, Dry Forest, Forest Savannah, and Savannah Woodland, a generic model and a model for Cerrado forest formation. Twelve 10 m × 10 m (100 m²) (National Forest Inventory) plots were used for each phytophysiognomy at different sites (regions) of the Federal District (FD) where trees had a diameter at breast height (DBH; 1.30 m) ≥5 cm in forest formations and a diameter at base height (Db; 0.30 m) ≥5 cm in savanna formations. Their diameters and heights were measured, they were cut and cubed, and the volume of each tree was obtained according to the Smalian methodology. Linear and nonlinear models were adjusted. Criteria for the selection of models were determined using correlation coefficients, the standard error of the estimates, and a graphical analysis of the residues. They were later validated by the chi-square test. The resultant models indicated that fit by specific phytophysiognomy was ideal; however, the generic and forest formation models exhibited similar performance to specific models and could be used in extensive areas of the Cerrado, where they represent a high potential for generalization. To further increase our understanding, similar research is recommended for the development of specific and generic models of the total volume in Cerrado areas. Full article
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<p>Venn diagram illustrating species sharing and exclusivity for different phytophysiognomies.</p>
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<p>Residual dispersal (<b>a</b>), observed and predicted values (<b>b</b>) and distribution of error classes (<b>c</b>) for Gallery Forest model (6).</p>
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<p>Residual dispersal (<b>a</b>), observed and predicted values (<b>b</b>) and distribution of error classes (<b>c</b>) for the Dry Forest model (3).</p>
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<p>Residual dispersal (<b>a</b>), observed and predicted values (<b>b</b>) and distribution of error classes (<b>c</b>) for the model (6) of Forest Savannah.</p>
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<p>Residual dispersal (<b>a</b>), observed and predicted values (<b>b</b>) and distribution of error classes (<b>c</b>) for the model (4) of Savannah Woodland.</p>
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<p>Residual dispersal (<b>a</b>), observed and predicted values (<b>b</b>) and distribution of error classes (<b>c</b>) for model (6) of generic model.</p>
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<p>Residual dispersal (<b>a</b>), observed and predicted values (<b>b</b>) and distribution of error classes (<b>c</b>) for the model (4) of Forest Formation.</p>
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<p>Location of sampling points of the different phytophysiognomies, Brazil.</p>
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18 pages, 742 KiB  
Article
The Impact of Planting Dates on the Performance of Soybean Varieties [Glycine max (L.) Merr.] in the Nigerian Savannas
by Osagie B. Eseigbe, Alpha Y. Kamara, Sani Miko, Lucky O. Omoigui, Reuben Solomon, Musibau A. Adeleke, Abdullahi I. Tofa and Jenneh F. Bebeley
Agronomy 2024, 14(10), 2198; https://doi.org/10.3390/agronomy14102198 - 25 Sep 2024
Viewed by 455
Abstract
Increasing delays in the onset of the rainy season and extended dry spells in the Nigerian savannas are complicating the determination of optimal planting dates for rain-fed crops, which increases risks for farmers. This study evaluated the impact of planting dates on soybean [...] Read more.
Increasing delays in the onset of the rainy season and extended dry spells in the Nigerian savannas are complicating the determination of optimal planting dates for rain-fed crops, which increases risks for farmers. This study evaluated the impact of planting dates on soybean [Glycine max (L.) Merr.] performance to identify optimal planting dates for different soybean varieties in two agroecological zones (AEZs) of Nigeria. The study involved six planting dates (15 June, 22 June, 29 June, 6 July, 13 July, and 20 July) and three soybean varieties (TGX-1835-10E, TGX-1951-3F, TGX-1904-6F). Results showed significant differences in growth and yield parameters based on location, variety, and planting date. In the Sudan savanna (SS), AEZ at BUK-Kano, optimal yields (>1500 kg ha−1) were achieved when planting TGX-1835-10E and TGX-1951-3F from 15 to 29 June and TGX-1904-6F on 15 June. Planting beyond 29 June reduces yields by 12–55% for TGX-1835-10E and 27–63% for TGX-1951-3F. For TGX-1904-6F, planting after 15 June reduces yields by 27–90%. In the Northern Guinea savanna (NGS) AEZ at Zaria, optimal yields (>1500 kg ha−1) were obtained when planting TGX-1835-10E and TGX-1951-3F from 15 June to 6 July, and TGX-1904-6F between 15 to 29 June. Delaying planting beyond these dates significantly reduced yields by 18–31% for TGX-1835-10E and 12–20% for TGX-1951-3F and 10–41% for TGX-1904-6F. Full article
(This article belongs to the Section Agroecology Innovation: Achieving System Resilience)
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<p>Monthly rainfall, minimum and maximum temperatures (TMin and TMax in °C) and solar radiation (SRAD) at BUK-KANO for (<b>a</b>) 2021 and (<b>b</b>) 2022 experimental years.</p>
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<p>Monthly rainfall, minimum and maximum temperatures (TMin and TMax in °C) and solar radiation (SRAD) at Samaru Zaria for (<b>a</b>) 2021 and (<b>b</b>) 2022 experimental years.</p>
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<p>Layout of impact of planting dates on three varieties of soybean.</p>
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14 pages, 1773 KiB  
Article
Faeces of Capybara (Hydrochoerus hydrochaeris) as a Bioindicator of Contamination in Urban Environments in Central-West Brazil
by Felipe Zampieri Vieira Batista, Igor Domingos de Souza, Diego Azevedo Zoccal Garcia, Daniela Granja Arakaki, Cláudia Stela de Araújo Medeiros, Marta Aratuza Pereira Ancel, Elaine Silva de Pádua Melo and Valter Aragão do Nascimento
Urban Sci. 2024, 8(4), 151; https://doi.org/10.3390/urbansci8040151 - 24 Sep 2024
Viewed by 735
Abstract
Along with exposure to parasites and other biological disease vectors, animal faeces can also contain heavy metals and metalloids. We quantified metals, metalloids, and non-metals in the faeces of capybara (Hydrochoerus hydrochaeris) that live in parks in the city of Campo [...] Read more.
Along with exposure to parasites and other biological disease vectors, animal faeces can also contain heavy metals and metalloids. We quantified metals, metalloids, and non-metals in the faeces of capybara (Hydrochoerus hydrochaeris) that live in parks in the city of Campo Grande (Brazil). Quantification of metalloids was obtained after acid digestion using an inductively coupled plasma optical emission spectrometer. Higher mean concentrations in mg/kg of aluminium (Al) (140.322), arsenic (As) (0.010), cadmium (Cd) (1.042), chromium (Cr) (26.866), cobalt (Co) (1.946), copper (Cu) (50.764), lead (Pb) (8.762), manganese (Mn) (291.469), molybdenum (Mo) (3.634), nickel (Ni) (5.475), and zinc (Zn) (100.027) were quantified in samples of faeces of capybara that live on the banks of a lagoon that receives input from streams that cross the city. According to the risk assessment, potential risks to the health of children and adults may occur due to the presence of Al, As, Cd, Co, Cu, and Mn through involuntary oral ingestion of faeces, via inhalation and dermal contact. The hazard index (HI) due to oral ingestion was greater than 1 for children and adults. Therefore, we believe that faeces of H. hydrochaeris can be considered as a bioindicator of environmental pollution in urban parks. Full article
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<p>Geographic location of Campo Grande/Brazil (<b>A</b>) Brazilian territory (<b>B</b>) State of Mato Grosso do Sul (MS), Brazilian Central-West (<b>C</b>) City of Campo Grande and sampling sites 1. Anhanduí Ecological Park; 2. Lago do Amor; 3. Sóter Ecological Park; and 4. Prosa State Park (Satellite image from Google Earth).</p>
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<p>Hazard index considering oral exposure for adults by contact with <span class="html-italic">H. hydrochaeris</span> faeces.</p>
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27 pages, 6924 KiB  
Article
GPP of a Chinese Savanna Ecosystem during Different Phenological Phases Simulated from Harmonized Landsat and Sentinel-2 Data
by Xiang Zhang, Shuai Xie, Yiping Zhang, Qinghai Song, Gianluca Filippa and Dehua Qi
Remote Sens. 2024, 16(18), 3475; https://doi.org/10.3390/rs16183475 - 19 Sep 2024
Viewed by 1098
Abstract
Savannas are widespread biomes with highly valued ecosystem services. To successfully manage savannas in the future, it is critical to better understand the long-term dynamics of their productivity and phenology. However, accurate large-scale gross primary productivity (GPP) estimation remains challenging because of the [...] Read more.
Savannas are widespread biomes with highly valued ecosystem services. To successfully manage savannas in the future, it is critical to better understand the long-term dynamics of their productivity and phenology. However, accurate large-scale gross primary productivity (GPP) estimation remains challenging because of the high spatial and seasonal variations in savanna GPP. China’s savanna ecosystems constitute only a small part of the world’s savanna ecosystems and are ecologically fragile. However, studies on GPP and phenological changes, while closely related to climate change, remain scarce. Therefore, we simulated savanna ecosystem GPP via a satellite-based vegetation photosynthesis model (VPM) with fine-resolution harmonized Landsat and Sentinel-2 (HLS) imagery and derived savanna phenophases from phenocam images. From 2015 to 2018, we compared the GPP from HLS VPM (GPPHLS-VPM) simulations and that from Moderate-Resolution Imaging Spectroradiometer (MODIS) VPM simulations (GPPMODIS-VPM) with GPP estimates from an eddy covariance (EC) flux tower (GPPEC) in Yuanjiang, China. Moreover, the consistency of the savanna ecosystem GPP was validated for a conventional MODIS product (MOD17A2). This study clearly revealed the potential of the HLS VPM for estimating savanna GPP. Compared with the MODIS VPM, the HLS VPM yielded more accurate GPP estimates with lower root-mean-square errors (RMSEs) and slopes closer to 1:1. Specifically, the annual RMSE values for the HLS VPM were 1.54 (2015), 2.65 (2016), 2.64 (2017), and 1.80 (2018), whereas those for the MODIS VPM were 3.04, 3.10, 2.62, and 2.49, respectively. The HLS VPM slopes were 1.12, 1.80, 1.65, and 1.27, indicating better agreement with the EC data than the MODIS VPM slopes of 2.04, 2.51, 2.14, and 1.54, respectively. Moreover, HLS VPM suitably indicated GPP dynamics during all phenophases, especially during the autumn green-down period. As the first study that simulates GPP involving HLS VPM and compares satellite-based and EC flux observations of the GPP in Chinese savanna ecosystems, our study enables better exploration of the Chinese savanna ecosystem GPP during different phenophases and more effective savanna management and conservation worldwide. Full article
(This article belongs to the Special Issue Remote Sensing of Savannas and Woodlands II)
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<p>Study area and the Yuanjiang (YJ) savanna flux tower site.</p>
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<p>Workflow of this study. The light blue rectangular boxes denote the key processes, and the dark green rectangular boxes denote the important data and result outputs.</p>
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<p>Variations in temperature (<b>a</b>) and precipitation (<b>b</b>) at the Yuanjiang station from 2015 to 2018.</p>
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<p>Time series of the daily GCC derived from phenocam images and HLS-based VIs (NDVI, LSWI, and EVI) at the Yuanjiang savanna site from September 2015 to December 2018. Because the Sentinel-2 satellite was launched in June 2015, the HLS time series data began in September 2015 after quality control.</p>
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<p>Daily GCC derived from phenocam images and MODIS-based VIs (NDVI, LSWI, and EVI) at the Yuanjiang savanna site from 2015 to 2018.</p>
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<p>Linear correlation coefficients between the HLS- (<b>a</b>–<b>c</b>) and MODIS-based VIs (<b>d</b>–<b>f</b>) and the flux observation-based GPP<sub>EC</sub>.</p>
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<p>Comparison between the interannual variations in the EC tower-derived gross primary production (GPP<sub>EC</sub>) and the simulated GPP (GPPvpm) from the two remote sensing data sources: (<b>a</b>) MODIS and (<b>b</b>) HLS.</p>
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<p>Linear comparisons of the tower-based gross primary production (EC) with the VPM GPP estimates for the HLS (HLS VPM) (<b>a</b>–<b>d</b>) and MODIS (MODIS VPM) data (<b>e</b>–<b>h</b>) from 2015 to 2018. R<sup>2</sup>: coefficient of determination; the fitting equation for y and x and 0 intercepts are provided.</p>
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<p>Comparison between the interannual variations in the tower-derived gross primary production (GPP<sub>EC</sub>) and the MODIS (MOD17A2)-based GPP.</p>
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<p>Example of a Yuanjiang savanna photograph processed with the xROI package (<b>a</b>) and 2015–2018 time series of the daily GCC in the Yuanjiang savanna (<b>b</b>). The three red masks denoting the ROI (<b>a</b>). The photo dates are 8 June 2015, and the file name is yj_2015_06_08_120412. The JPG image follows the phenocam convention. The GCC index is a dimensionless, calculated value extracted from digital photographs over the 2015–2018 period (<b>b</b>).</p>
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<p>Linear regression equations with an intercept of 0 for the HLS VPM simulations compared with the EC data during the different phenophases from 2015 to 2018 (<b>a</b>–<b>d</b>) for the green-up phenophase of each year and (<b>e</b>–<b>h</b>) for the green-down phenophase of each year.</p>
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<p>Linear regression equations with an intercept of 0 for the MODIS VPM GPP simulations compared with the EC data during the different phenophases from 2015 to 2018 (<b>a</b>–<b>d</b>) for the green-up phenophase of each year and (<b>e</b>–<b>h</b>) for the green-down phenophase of each year.</p>
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<p>Linear regression equations with an intercept of 0 for the MOD17A2 GPP simulations compared with the EC data during the different phenophases from 2015 to 2018 (<b>a</b>–<b>d</b>) for the green-up phenophase of each year and (<b>e</b>–<b>h</b>) for the green-down phenophase of each year.</p>
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8 pages, 866 KiB  
Brief Report
Presence and Absence of Beehives as a Management Tool for Reducing Elephant-Induced Tree Mortality
by Robin M. Cook and Michelle D. Henley
Diversity 2024, 16(9), 577; https://doi.org/10.3390/d16090577 - 13 Sep 2024
Viewed by 1007
Abstract
Beehives have previously been used to protect large trees from elephant impact in sub-arid savannas, thus improving the persistence of large trees as habitats for other species. This brief report aimed to investigate the effectiveness of the presence and absence of beehives as [...] Read more.
Beehives have previously been used to protect large trees from elephant impact in sub-arid savannas, thus improving the persistence of large trees as habitats for other species. This brief report aimed to investigate the effectiveness of the presence and absence of beehives as a management tool for reducing elephant-induced tree mortality. The study was conducted in three phases: Phase 1 (2015–2020) involved actively maintaining beehives on marula trees (Sclerocarya birrea subsp. caffra), Phase 2 (2020–2022) the systematic reduction in the number of active beehives, and Phase 3 (2022–2024) the removal of all beehives. The persistence rates of the trees with beehives were compared to those without beehives. We found that beehives significantly improved the persistence of the trees in the presence of elephants. During Phase 1, only 10% of the trees with beehives died compared to 34% of the trees with no beehives. In Phase 2, with a reduced number of active beehives, the mortality rates increased slightly for both trees with beehives and those without. However, in Phase 3, after the removal of all the beehives, the mortality rates significantly increased for all the trees monitored as part of the study. We also found that the mortality rate of the original trees with no beehives increased when beehives were removed from the study site, whilst the mortality rate of the original beehive trees without beehives in Phase 3 (8.7%) surpassed that of the 8.1% prior to the hanging of beehives. These findings highlight the effectiveness of beehives as a tree protection method against elephant impact and how beehives can improve the persistence of tree populations co-occurring with elephants. Full article
(This article belongs to the Section Biodiversity Conservation)
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<p>(<b>a</b>) Location of the Jejane Private Nature Reserve (JPNR) within the Associated Private Nature Reserves (APNR) of South Africa, and (<b>b</b>) a visual illustration of Phases 1–3, indicating the varying levels of beehive occupancy per phase.</p>
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<p>Persistence proportions of the marula trees with beehives present and absent across Phases 1–3 of the study within the Jejane Private Nature Reserve (JPNR) within the Associated Private Nature Reserves (APNR) of South Africa. ** <span class="html-italic">p</span> &lt; 0.01.</p>
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Article
Biomonitoring of Waters and Tambacu (Colossoma macropomum × Piaractus mesopotamicus) from the Amazônia Legal, Brazil
by Karuane Saturnino da Silva Araújo, Thiago Machado da Silva Acioly, Ivaneide Oliveira Nascimento, Francisca Neide Costa, Fabiano Corrêa, Ana Maria Gagneten and Diego Carvalho Viana
Water 2024, 16(18), 2588; https://doi.org/10.3390/w16182588 - 12 Sep 2024
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Abstract
Fish farming is increasingly important globally and nationally, playing a crucial role in fish production for human consumption. Monitoring microbiological and chemical contaminants from water discharge is essential to mitigate the risk of contaminating water and fish for human consumption. This study analyzes [...] Read more.
Fish farming is increasingly important globally and nationally, playing a crucial role in fish production for human consumption. Monitoring microbiological and chemical contaminants from water discharge is essential to mitigate the risk of contaminating water and fish for human consumption. This study analyzes the physicochemical and E. coli parameters of water and tambacu fish muscles (Colossoma macropomum × Piaractus mesopotamicus) in Western Maranhão, Brazil. It also includes a qualitative characterization of zooplankton in the ponds. Samples were collected from tambacu ponds in a dam system fed by natural watercourses from the Tocantins River tributaries, located at the connection of the Brazilian savanna and Amazon biomes. The physicochemical and E. coli parameters of water did not meet national standards. The zooplankton community included Rotifera, Cladocera, Copepoda, and Protozoa representatives, with no prior studies on zooplankton in the region, making these findings unprecedented. The biological quality of freshwater is crucial in fish farming, as poor quality can lead to decreased productivity and fish mortality, raising significant food safety concerns. The water quality studied is related to the potential influence of untreated wastewater as a source of contamination, leaving the studied region still far from safe water reuse practices. The findings on chemical and E. coli contamination of fish farming waters concern human health and emphasize the need for appropriate regulations. Full article
(This article belongs to the Section Water Quality and Contamination)
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<p>Location and key characteristics of the study area, Maranhão, Brazil.</p>
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<p>Specimen of tambacu (<span class="html-italic">Colossoma macropomum × Piaractus mesopotamicus</span>) from the Amazônia legal, Brazil.</p>
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<p>Zooplankton species sampled in the water of tambacu fish farming tanks.</p>
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