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18 pages, 3052 KiB  
Article
Effects of Vegetation on Bird Communities and Bird–Plant Interactions in Urban Green Areas of Riparian Forests in Brazil That Have Undergone Ecological Restoration
by Dayana Nascimento Carvalho, Eduardo Soares Calixto and Kleber Del-Claro
Diversity 2025, 17(3), 149; https://doi.org/10.3390/d17030149 - 22 Feb 2025
Viewed by 488
Abstract
Urbanization replaces natural vegetation for city expansion, impacting environmental and climatic variables that affect the health of the human population and fauna. These changes affect important groups such as birds, given their greater sensitivity to anthropogenic alterations, especially when we understand these effects [...] Read more.
Urbanization replaces natural vegetation for city expansion, impacting environmental and climatic variables that affect the health of the human population and fauna. These changes affect important groups such as birds, given their greater sensitivity to anthropogenic alterations, especially when we understand these effects on a large scale, considering countries such as Brazil, which represents the third country with the greatest diversity of bird species in the world. Conversely, green spaces like urban parks, tree-lined avenues, and riparian forests seem to foster biodiversity conservation. Here, we analyze the effects of vegetation on bird communities and bird–plant interactions in urban riparian areas that have undergone ecological restoration. The study was carried out between January and October 2019 in two restored urban areas of Uberlândia, Brazil. Results showed that the richness of birds observed between the two areas was Praia Clube (n = 86) and Parque Linear Rio Uberabinha (n = 80). The most representative trophic guilds in the areas, with the highest proportion in their relative abundances during both seasons, were granivores, omnivores, insectivores, and frugivores. Composition varied significantly between areas as a function of the plant community, particularly when considering the interaction between season and area (ANOSIM: R = 0.19; Stress = 0.10; p = 0.008). In environments dominated by generalist and synanthropic species (Eared Dove, Picazuro Pigeon), effective planning and management of green areas are crucial. It is important to acknowledge that certain bird species depend on specific habitats, such as riparian forests, and that specific plant species within these areas are vital for specialized bird species, such as species endemic to the Brazilian Savanna or Cerrado and restricted to Brazil (White-striped Warbler) and species in vulnerable categories globally (Bare-faced Curassow). Therefore, restoration efforts in degraded areas should be carefully planned to restore interactions and conserve biodiversity effectively. Full article
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Figure 1

Figure 1
<p>Compared plant composition in relation to the study area (PC = purple, square and PL= red, circle). NMDS biplot of plant species variation between areas. Ellipses indicate a 95% confidence interval.</p>
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<p>Rarefaction (solid line segment) and extrapolation (dotted line segments) sampling curves with 95% confidence intervals (shaded areas) for bird species data in two areas, PC (rainy = purple, triangle; dry = pink, circle) and PL (rainy = red, cross; dry = orange, square), separately by order diversity: q = 0 (species richness), q = 1 (Shannon’s exponential index) and q = 2 (inverse of Simpson’s index). On the X axis (numbers of individuals), the value 6000 represents the extrapolation limit established during the analysis. The internal numbers in the figures and the following curves indicate the observed values and the estimated diversity of bird species comparing two areas.</p>
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<p>Circular diagrams of the relationship between trophic guilds and study areas: PC ((<b>A</b>): rainy, purple; (<b>B</b>): dry, pink) and PL ((<b>C</b>): rainy, red; (<b>D</b>): dry, orange) weighted by the relative abundance (%) of birds.</p>
Full article ">Figure 4
<p>Circular diagrams of the interaction between the species of birds and plants, PC (<b>A</b>) and PL (<b>B</b>), and the resources exploited by the species of birds between the seasons, PC (rainy (<b>C</b>) and dry (<b>E</b>)) and PL ((<b>D</b>) rainy and (<b>F</b>) dry). Bird species and exploited resources are represented in bright colors, and plant species are represented in gray with the indications * regional native (green), non-regional native (blue), and exotic (red). The lines (connection and thickness) denote the interaction and the number of records (based on abundance) of bird species in search of resources in the plant species. Abbreviations for scientific names of plants: CS1 = <span class="html-italic">Cestrum schlechtendalii</span>, CS2 = <span class="html-italic">Ceiba speciosa</span>, CU = <span class="html-italic">Croton urucurana</span>, CV = <span class="html-italic">Callistemon viminalis</span>, DR = <span class="html-italic">Delonix regia</span>, EJ = <span class="html-italic">Eriobotrya japonica</span>, ES = <span class="html-italic">Erythrina speciosa</span>, FE = <span class="html-italic">elastic ficus</span>, FG = <span class="html-italic">Ficus guaranitica</span>, HC = <span class="html-italic">Handroanthus chrysotrichus</span>, HI = <span class="html-italic">Handroanthus impetiginosus</span>, IL = <span class="html-italic">Inga laurina</span>, IS = <span class="html-italic">Inga sessilis</span>, MC = <span class="html-italic">calabura muntingia</span>, MF = <span class="html-italic">Microlobius foetidus</span>, MO = <span class="html-italic">Moringa oleifera</span>, MN = <span class="html-italic">More nigra</span>, PG = <span class="html-italic">Psidium guajava</span>, SC = <span class="html-italic">Spathodea campanulate</span>, ST = <span class="html-italic">Schinus terebinthifolia</span>. Abbreviations for scientific names of birds: AF = <span class="html-italic">Amazilia fimbriata</span>, BC = <span class="html-italic">Brotogeris chiriri</span>, CA = <span class="html-italic">Crotophaga ani</span>, CF = <span class="html-italic">Coereba flaveola</span>, CL = <span class="html-italic">Chlorostilbon lucidus</span>, CR = <span class="html-italic">Chrysomus ruficapillus</span>, DN = <span class="html-italic">Diopsittaca nobilis</span>, EA = <span class="html-italic">Eupsittula aurea</span>, EC = <span class="html-italic">Euphonia chlorotica</span>, EM = <span class="html-italic">Eupetomena macroura</span>, ES = <span class="html-italic">Elaenia spectabilis</span>, HC = <span class="html-italic">Hylocharis chrysura</span>, HL = <span class="html-italic">Herpsilochmus longirostris</span>, IC = <span class="html-italic">Icterus croconotus</span>, IP = <span class="html-italic">Icterus pyrrhopterus</span>, MT = <span class="html-italic">Myiarchus tyrannulus</span>, PL = <span class="html-italic">Psittacara leucophthalmus</span>, TP = <span class="html-italic">Tangara palmarum</span>, TS = <span class="html-italic">Tangara sayaca</span>. Acronyms for resources: FL = Flower, FR = Fruit, NE = Nectar, SE = Seed.</p>
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<p>Bird composition compared in relation to the study area (PC and PL) and between seasons (PC: rainy = purple, square; dry = pink, circle. PL: rainy = red, triangle; dry = orange, rhombus). Ellipses indicate a 95% confidence interval.</p>
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<p>Biplot canonical correspondence analysis (CCA) of floristic variables and climate variables (represented by arrows, black) and bird community, response variable (represented by triangles, randomly colored). Proportion of total explained variance: axes 1 = 22%; axes 2 = 12%.</p>
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21 pages, 4764 KiB  
Article
The Importance of Urban Greening Spaces for Avian Communities in an Urbanized Landscape
by Grzegorz Kopij
Land 2025, 14(2), 400; https://doi.org/10.3390/land14020400 - 14 Feb 2025
Viewed by 344
Abstract
Island ecology plays an important role in explaining various ecological and evolutionary processes. Small, isolated oceanic islands, exemplified by the Azores Archipelago, are especially vulnerable to adverse environmental conditions and human impact. The study aims to evaluate the impact of urbanization, especially the [...] Read more.
Island ecology plays an important role in explaining various ecological and evolutionary processes. Small, isolated oceanic islands, exemplified by the Azores Archipelago, are especially vulnerable to adverse environmental conditions and human impact. The study aims to evaluate the impact of urbanization, especially the urban greening space, on the structure and dynamics of avian communities associated with various landforms in an urbanized landscape in one of the nine islands of the Azores Archipelago, São Miguel Island, in the northeast Atlantic Ocean. Samples were collected in the second half of April 2024. The line transect method (43 transects with a total of 37.4 km) was employed to count all bird species breeding in different landforms distinguished in the city: coastal land, urbanized land, rural land, and urban greening space. The obtained results showed that the number of breeding species was much higher in urban greening spaces (n = 20) than in the other lands (n = 10–14 species). Both cumulative dominance and dominance indices were much lower in urban greening space than in the other landforms. The Sørensen Index of Similarity between the four main land categories distinguished in the city varied between 0.62 and 0.96, being the lowest between the coastal and urban greening space, and the highest between the urbanized and rural lands. Two main feeding guilds were distinguished in the study area: granivores and insectivores. The former guild clearly dominated over the latter in all major land categories distinguished. Clearly, the proportion of granivores increased with urbanization. Also, two nesting guilds were distinguished: buildings and trees/shrubs. The former was dominant in all land categories except for the urban greening space where the tree/shrub nesting guild was more numerous than the building guild. The tree/shrub guild declined with urbanization. A general trend was recorded: the higher the level of urbanization, the lower the percentage of urban greening space, and in consequence, the lower the number of bird species and diversity indices, but the higher the cumulative dominance and dominance indices. The overall density of birds remains, however, distinctively similar. In the future, data on the population densities and dominance of particular species should be collected in urbanized landforms in other towns of the Azores Archipelago and Macaronesia at large. Full article
(This article belongs to the Special Issue Species Vulnerability and Habitat Loss II)
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Figure 1
<p>(<b>A</b>): The satellite image of the study area (Ponta Delgada); (<b>B</b>): spatial distribution of transects. (1–40) and their grouping: (<b>A</b>)—coastal built-up land, (<b>B</b>)—residential suburbs (80–90% of the surface is built-up) with an admixture of green areas and some agricultural lands, (<b>C</b>)–city center, densely-built-up (80–90%), with sparse tree vegetation, (<b>D</b>)—city center, densely built-up (70–80%), well timbered, (<b>E</b>)—residential suburbs (60–70%), with an admixture of urban greening space and some open tarred lands, (<b>F</b>)—residential suburbs, (50–60%), with an admixture of pastures and arable lands, (<b>G</b>)—residential suburbs, (50–60%), with an admixture of gardens, pastures and parkland, (<b>H</b>)—industry area (70–80%). Three transects in rural land (41, 42, and 43) were designed in Arrifes, further to the east (viz. <a href="#land-14-00400-f002" class="html-fig">Figure 2</a>A).</p>
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<p>Different landforms in the urbanized landscape of Ponta Delgada: (<b>A</b>): rural land, (<b>B</b>): urban land, residential loosely built-up land, (<b>C</b>): urban greening space: Borges municipal garden; (<b>D</b>): urban land, city center; (<b>E</b>): urban greening space: Canto botanic garden; (<b>F</b>): coastal densely built-up land.</p>
Full article ">Figure 2 Cont.
<p>Different landforms in the urbanized landscape of Ponta Delgada: (<b>A</b>): rural land, (<b>B</b>): urban land, residential loosely built-up land, (<b>C</b>): urban greening space: Borges municipal garden; (<b>D</b>): urban land, city center; (<b>E</b>): urban greening space: Canto botanic garden; (<b>F</b>): coastal densely built-up land.</p>
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<p>The proportion of granivorous and insectivorous birds in the main landforms in the urbanized landscape of the city of Ponta Delgada.</p>
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<p>The proportion of granivorous and insectivorous birds in various subcategories of the built-up lands (A–H, as in <a href="#land-14-00400-f001" class="html-fig">Figure 1</a>B) in the city of Ponta Delgada.</p>
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<p>The proportion of two nesting guilds of birds in the main landforms in the urbanized landscape of the city of Ponta Delgada.</p>
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<p>The proportion of two nesting guilds of birds in various subcategories of the built-up lands (A–H, as in <a href="#land-14-00400-f001" class="html-fig">Figure 1</a>B) in the city of Ponta Delgada).</p>
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15 pages, 9733 KiB  
Article
Vegetation Affects the Responses of Canopy Spider Communities to Elevation Gradients on Changbai Mountain, China
by Pengfeng Wu, Lingxu Xiang, Qiang Zhao, Shuyan Cui, Abid Ali, Donghui Wu and Guo Zheng
Insects 2024, 15(3), 154; https://doi.org/10.3390/insects15030154 - 24 Feb 2024
Cited by 1 | Viewed by 2542
Abstract
Forest canopies, an essential part of forest ecosystems, are among the most highly threatened terrestrial habitats. Mountains provide ideal conditions for studying the variation in community structure with elevations. Spiders are one of the most abundant predators of arthropods in terrestrial ecosystems and [...] Read more.
Forest canopies, an essential part of forest ecosystems, are among the most highly threatened terrestrial habitats. Mountains provide ideal conditions for studying the variation in community structure with elevations. Spiders are one of the most abundant predators of arthropods in terrestrial ecosystems and can have extremely important collective effects on forest ecosystems. How the diversity and composition of canopy spider communities respond to elevation changes in temperate forests remains poorly understood. In this study, we collected canopy spiders from four elevation sites (800 m, 1100 m, 1400 m, and 1700 m) on Changbai Mountain using the fogging method in August 2016. With the methods of ANOVA analysis, transformation-based redundancy analysis, and random forest analysis, we explored the responses of canopy spider communities to elevation. In total, 8826 spiders comprising 81 species were identified and the most abundant families were Thomisidae, Clubionidae, Linyphiidae, and Theridiidae (77.29% of total individuals). Species richness decreased whereas evenness increased with increasing elevation, indicating that elevation has an important impact on community structure. The pattern of absolute abundance was hump shaped with increasing elevation. We found that the community compositions at the three taxonomic levels (species, family, and guild) along the elevation gradient were obviously altered and the variation in community composition was higher at low-elevation sites than at high-elevation sites. There were 19 common species (23.46%) among the four elevations. Regression and RDA results showed that vegetation variables contributed to the variation in the diversity and composition of canopy spiders. Furthermore, the influence of factors would be weakened with the taxonomic level increasing. Therefore, our findings greatly highlight the important role of vegetation in the diversity and composition of canopy spiders and the influence is closely related to the taxonomic level. Full article
(This article belongs to the Collection Insects in Mountain Ecosystems)
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Figure 1
<p>Sampling sites on Changbai Mountain, China. (<b>A</b>) Location. (<b>B</b>,<b>C</b>) Fogging process and funnel-like trays. Elevation: Site 1 = 800 m, Site 2 = 1100 m, Site 3 = 1400 m, and Site 4 = 1700 m.</p>
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<p>Diversity of canopy spiders to elevation changes on Changbai Mountain, China. (<b>A</b>) Species richness (<sup>0</sup><span class="html-italic">D</span>). (<b>B</b>) Exponential Shannon diversity (<sup>1</sup><span class="html-italic">D</span>). (<b>C</b>) Inverse Simpson diversity (<sup>2</sup><span class="html-italic">D</span>). (<b>D</b>) Inverse Berger-Parker (<sup>3</sup><span class="html-italic">D</span>). (<b>E</b>) Pielou evenness index. Error bar means standard error (S.E.). The number of replicates was 4 (<span class="html-italic">n</span> = 4). Lowercase letters indicate significant difference for multiple comparisons using LSD.</p>
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<p>Relative abundance of species ((<b>A</b>), absolute abundance greater than 4%), family ((<b>B</b>), top four families), and guild (<b>C</b>) of canopy spiders to elevation changes on Changbai Mountain, China. Error bar means standard error (S.E.). The number of replicates was 4 (<span class="html-italic">n</span> = 4). Lowercase letters indicate significant differences for multiple comparisons using LSD. The tests of species in <a href="#insects-15-00154-f003" class="html-fig">Figure 3</a>A were examined using the Kruscal–Wallis test followed by the DUNN test for multiple comparisons.</p>
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<p>Variation in the community composition of canopy spiders among elevations on Changbai Mountain, China. (<b>A</b>) Bray–Curtis dissimilarity within the four elevations. (<b>B</b>) NMDS for canopy spider communities based on Bray–Curtis dissimilarity. The 95% confidence ellipses around group centroids. The number of replicates was 6 (<span class="html-italic">n</span> = 6) in <a href="#insects-15-00154-f004" class="html-fig">Figure 4</a>A. The dashed line means three levels of dissimilarity, with the Bray–Curtis distance being 0.25, 0.5, and 0.75 in <a href="#insects-15-00154-f004" class="html-fig">Figure 4</a>A.</p>
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<p>Responses of absolute abundance (<b>A</b>), species richness (<b>B</b>), and exponential Shannon diversity (<b>C</b>) of canopy spiders to vegetation factors and their relative importance on species richness (<b>D</b>) on Changbai Mountain, China. Light blue bars represent significant levels at <span class="html-italic">p</span> &lt; 0.05 and green bars represent significant levels at <span class="html-italic">p</span> &gt; 0.05 in <a href="#insects-15-00154-f005" class="html-fig">Figure 5</a>D. **, <span class="html-italic">p</span> &lt; 0.01; *, <span class="html-italic">p</span> &lt; 0.05; ns, no significance.</p>
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<p>Habitat factors influencing the community composition of canopy spiders based on RDA on Changbai Mountain, China. (<b>A</b>) Species level. (<b>B</b>) Family level. (<b>C</b>) Guild level. Abbreviations: ELE = elevation, TH = tree height, SH = shrub height, TC = tree coverage, SC = shrub coverage, HC = herb coverage. The 95% confidence ellipses around group centroids. Significant influencing factors derived from permutational tests are shown (<span class="html-italic">p</span> &lt; 0.05).</p>
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<p>Venn diagram based on the composition of canopy spiders among elevations on Changbai Mountain, China. The different colors represent different elevations, and the different numbers indicate the shared and non-shared species among elevations.</p>
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16 pages, 1794 KiB  
Article
Bat Species Diversity and Abundance of Trophic Guilds after a Major Hurricane along an Anthropic Disturbance Gradient
by Luz María Sil-Berra, Cornelio Sánchez-Hernández, María de Lourdes Romero-Almaraz and Víctor Hugo Reynoso
Diversity 2022, 14(10), 818; https://doi.org/10.3390/d14100818 - 29 Sep 2022
Cited by 1 | Viewed by 2364
Abstract
The frequency and intensity of hurricanes have increased with climate change, and their effects on most taxa are not known. We analyzed a species diversity of bats in three locations with different regimes of anthropic disturbance. We assessed the effect of the season [...] Read more.
The frequency and intensity of hurricanes have increased with climate change, and their effects on most taxa are not known. We analyzed a species diversity of bats in three locations with different regimes of anthropic disturbance. We assessed the effect of the season and post-hurricane time on the abundance of trophic guilds in coastal Jalisco, México, during the two years following Hurricane Patricia (category 4). During a sampling effort of 15,629.76 m2 of netting, we captured 790 bats of 21 species. The species diversity was higher in the site with the highest proportion of primary tropical deciduous forest and was higher in 2016 than in 2017; the species composition did not differ greatly between the two years. The abundance of bats in various trophic guilds varied relative to the four climatic seasons. The general abundance of bats, frugivores-omnivores, and insectivores showed a significant increasing trend over time after the hurricane, which may indicate a recovery of the ecosystem or an abundance of early-successional fruiting plants. The results also confirm that species diversity recovers faster in a conserved forest. Thus, it is important to conserve natural areas to mitigate the effects of major disturbances. Full article
(This article belongs to the Section Biodiversity Loss & Dynamics)
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Figure 1
<p>Diversity orders q = 0, 1, and 2 based in number of individuals (<b>a</b>–<b>c</b>) and sampling coverage (<b>d</b>–<b>f</b>) for three locations during two years of fieldwork.</p>
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<p>Interpolation (continuous lines) and extrapolation curves (discontinuous lines) of species diversity orders q = 0, 1 and 2, based in number of individuals (<b>left panel</b>) and sampling coverage (<b>right panel</b>) for Chamela in 2016 (blue line) and 2017 (purple line).</p>
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<p>Rank-abundance curves of bat species captured in 2016 and 2017 in Chamela, Jalisco. 1: <span class="html-italic">Artibeus jamaicensis</span>, 2: <span class="html-italic">Desmodus rotundus</span>, 3: <span class="html-italic">A. lituratus</span>, 4: <span class="html-italic">Dermanura phaeotis</span>, 5: <span class="html-italic">Pteronotus mexicanus</span>, 6: <span class="html-italic">Glossophaga mutica</span>, 7: <span class="html-italic">Leptonycteris yerbabuenae</span>, 8: <span class="html-italic">G. commissarisi</span>, 9: D. <span class="html-italic">tolteca</span>, 10: <span class="html-italic">Mormoops megalophylla</span>, 11: <span class="html-italic">P. psilotis</span>, 12: <span class="html-italic">P. fulvus</span>, 13: <span class="html-italic">G. morenoi</span>, 14: <span class="html-italic">Sturnira parvidens</span>, 15: <span class="html-italic">Rhogeessa parvula</span>, 16: <span class="html-italic">Natalus mexicanus</span>, 17: <span class="html-italic">Centurio senex</span>, 18: <span class="html-italic">Lasiurus frantzii</span>.</p>
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<p>Differences in number of captures and relative abundance between 2016 and 2017 of captured species in Chamela. Only names of species with the greatest changes are included. Some of the dots in the cluster of points around zero represent multiple species.</p>
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<p>Seasonal variation in abundance of bats (number of captures), total (<b>a</b>) and by trophic guilds (<b>b</b>–<b>f</b>), in accordance with selected models throughout GLMs. E-R: Early rainy, L-R: Late rainy, E-D: Early dry, L-D: Late dry. Details are shown in <a href="#app1-diversity-14-00818" class="html-app">Table S1 of Supplementary Materials</a>.</p>
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<p>Post-hurricane trends in the abundance of bats, total (<b>a</b>) and by trophic guilds (<b>b</b>–<b>f</b>), from March 2016 to December 2017. Sen’s slope (red line) adjusted to smoothed curve (blue line).</p>
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17 pages, 1865 KiB  
Article
A Nematode Community-Based Integrated Productivity Efficiency (IPE) Model That Identifies Sustainable Soil Health Outcomes: A Case of Compost Application in Carrot Production
by Alemayehu Habteweld, Alexandra N. Kravchenko, Parwinder S. Grewal and Haddish Melakeberhan
Soil Syst. 2022, 6(2), 35; https://doi.org/10.3390/soilsystems6020035 - 11 Apr 2022
Cited by 1 | Viewed by 3112
Abstract
Percent soil organic matter (SOM), pH and crop yield are among the biophysicochemical process-driven soil health indicators (SHIs). However, identifying sustainable soil health conditions using these SHIs is limited due to the lack of Integrated Productivity Efficiency (IPE) models. We define IPE as [...] Read more.
Percent soil organic matter (SOM), pH and crop yield are among the biophysicochemical process-driven soil health indicators (SHIs). However, identifying sustainable soil health conditions using these SHIs is limited due to the lack of Integrated Productivity Efficiency (IPE) models. We define IPE as a concept that identifies best-to-worst-case soil health outcomes by assessing the effect of agronomic practices on weighted abundance of functional guilds (WAFG) of beneficial soil organisms and SHIs simultaneously. Expressing WAFG of all beneficial nematodes (x-axis) and SHIs (y-axis) as a percent of untreated control and regression of x and y reveals four quadrants describing worst-to-best-case outcomes for soil health and sustainability. We tested the effects of composted cow manure (AC) and plant litter (PC) applied at 135 (1×), 203 (1.5×), and 270 (2×) kg N/ha on WAFG, SOM, pH, and yield in a sandy clay loam field of a processing carrot cultivar over three growing seasons. Untreated control and urea at 1× served as experimental controls. Data that varied by time and were difficult to make sense of were separated into sustainable, unsustainable, or requiring specific modification to be sustainable categories by the IPE model. Within the sustainable category, all AC treatments and 2× rate of PC treatments had the best integrated efficiency outcomes across the SHIs. The IPE model provides a platform where other biophysicochemical process-driven SHIs could be integrated. Full article
(This article belongs to the Special Issue Soil Metabolism and Biogenic Emissions of CO2 and N2O)
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Figure 1
<p>Modified fertilizer use efficiency (FUE) model analysis quadrants separating best (green), worst (red) and variable (olive green) outcomes of ecosystem service (ES) and beneficial nematodes (BN; [<a href="#B9-soilsystems-06-00035" class="html-bibr">9</a>]) as indicators of the biological component of the SFW. Increased (▲) and decreased (▼) responses and what they mean (=) are indicated. 100% on either axis is a control.</p>
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<p>A conceptual illustration of the Integrated Production Efficiency (IPE) model that uses the relationship between changes in Weighted abundance of functional guilds (WAFG, <span class="html-italic">x</span>-axis) of nematodes and soil health indicators (SHI, <span class="html-italic">y</span>-axis) expressed as a percent of control to identify outcomes from best-to-worst cases for integrated efficiency for WAFG, SHI, and soil health and overall sustainability of the outcomes. Increases (▲) and decreases (▼) in the SHI and WAFG are indicated. Data points that fall above the controls (100%) will show an increase/improvement in tested SHIs (A and B) and WAFG (B and D). Data points in Quadrant B where a desired SHI and WAFG increase would be best-case scenario for soil health and sustainability of the outcome. Data points in Quadrant C where SHI and WAFG decrease would be worst-case scenario for soil health, environmental and economic outcomes and unsustainable. Data points in Quadrants A and D provide a choice of improving WAFG and SHI, respectively, to achieve soil health.</p>
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<p>Integrated Production Efficiency (IPE) of amending sandy clay loam soil with either animal (AC) or plant (PC) based compost applied at 135, 203 or 270 kg N/ha planted with processing cultivar on organic matter (<span class="html-italic">y</span>-axis) and weighted abundance of functional guilds (WAFG, <span class="html-italic">x</span>-axis) of nematodes at planting in May 2012 (May 12) and harvest in October 2012 (Oct 12) and 2013 (Oct 13) growing seasons fitted to the IPE model. Numbers 1–3 refer PC at a rate of 135, 203 and 270 kg N/ha, respectively and 4–6 refer AC at a rate of 135, 203 and 270 kg N/ha, respectively, 7 and 8 refer urea and non-amended check, respectively. * Treatments with subscripts and superscripts asterisks (*) indicate significantly different from 100% for WAFG and soil organic matter, respectively, using one-tailed <span class="html-italic">t</span>-test at α = 0.05. The soil amendment rates and the organic matter data presented here are the same as those in <a href="#app1-soilsystems-06-00035" class="html-app">Table S1</a>. The WAFG data presented here are the same as those in <a href="#soilsystems-06-00035-t001" class="html-table">Table 1</a>.</p>
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<p>Integrated Production Efficiency (IPE) of amending sandy clay loam soil with either animal (AC) or plant (PC) based compost applied at 135, 203 or 270 kg N/ha planted with processing cultivar on soil pH (<span class="html-italic">y</span>-axis) and weighted abundance of functional guilds (WAFG, <span class="html-italic">x</span>-axis) of nematodes at planting in May 2012 (May-12) and harvest in October 2012 (Oct-12) and 2013 (Oct-13) growing seasons fitted the IPE model. Numbers 1–3 refer PC at a rate of 135, 203 and 270 kg N/ha, respectively and 4–6 refer AC at a rate 135, 203 and 270 kg N/ha, respectively, 7 and 8 refer urea and non-amended check, respectively. * Treatments with subscripts and superscripts asterisks (*) indicate significantly different form 100% for WAFG and soil pH, respectively, using one-tailed <span class="html-italic">t</span>-test at α = 0.05. The soil amendment rates and the soil pH data presented here are the same as those in <a href="#app1-soilsystems-06-00035" class="html-app">Table S2</a>. The WAFG data presented here are the same as those in <a href="#soilsystems-06-00035-t001" class="html-table">Table 1</a>.</p>
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<p>Integrated Production Efficiency (IPE) of amending sandy clay loam soil with either animal (AC) or plant (PC) based compost applied at 135, 203 or 270 kg N/ha on marketable carrot (<span class="html-italic">y</span>-axis) and weighted abundance of functional guilds (WAFG, <span class="html-italic">x</span>-axis) of nematodes at harvest in October 2012 (Oct-12), 2013 (Oct-13) and 2014 (Oct-14) growing seasons fitted to the IPE model. Numbers 1–3 refer PC at a rate of 135, 203 and 270 kg N/ha, respectively and 4–6 refer AC at a rate 135, 203 and 270 kg N/ha, respectively, 7 and 8 refer urea and non-amended check, respectively. * Treatments with subscripts and superscripts asterisks (*) indicate significantly different form 100% for WAFG and marketable carrots, respectively, using one-tailed t-test at α = 0.05. The soil amendment rates and the marketable carrot data presented here are the same as those in <a href="#app1-soilsystems-06-00035" class="html-app">Table S3</a>. The WAFG data presented here are the same as those in <a href="#soilsystems-06-00035-t001" class="html-table">Table 1</a>.</p>
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<p>Integrated Production Efficiency (IPE) of amending sandy clay loam soil with either animal (AC) or plant (PC) based compost applied at 135, 203 or 270 kg N/ha on unmarketable carrot (<span class="html-italic">y</span>-axis) and weighted abundance of functional guilds (WAFG, <span class="html-italic">x</span>-axis) of nematodes at harvest in October 2012 (Oct-12), 2013 (Oct-13) and 2014 (Oct-14) growing seasons fitted to the IPE model. Numbers 1–3 refer PC at a rate of 135, 203 and 270 kg N/ha, respectively and 4–6 refer AC at a rate 135, 203 and 270 kg N/ha, respectively, 7 and 8 refer urea and non-amended check, respectively. * Treatments with subscripts and superscripts asterisks (*) indicate significantly different form 100% for WAFG and unmarketable carrots, respectively, using one-tailed t-test at α = 0.05. The soil amendment rates and the unmarketable carrot data presented here are the same as those in <a href="#app1-soilsystems-06-00035" class="html-app">Table S4</a>. The WAFG data presented here are the same as those in <a href="#soilsystems-06-00035-t001" class="html-table">Table 1</a>.</p>
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18 pages, 1492 KiB  
Article
Food Web Structure and Trophic Interactions Revealed by Stable Isotope Analysis in the Midstream of the Chishui River, a Tributary of the Yangtze River, China
by Qiang Qin, Fubin Zhang, Fei Liu, Chunling Wang and Huanzhang Liu
Water 2021, 13(2), 195; https://doi.org/10.3390/w13020195 - 15 Jan 2021
Cited by 13 | Viewed by 4563
Abstract
Understanding energy flow and nutrient pathways is crucial to reveal the dynamics and functions of riverine ecosystems and develop appropriate conservation strategies. In this study, we utilized stable isotopes of δ13C and δ15N to examine the fundamental characteristics of [...] Read more.
Understanding energy flow and nutrient pathways is crucial to reveal the dynamics and functions of riverine ecosystems and develop appropriate conservation strategies. In this study, we utilized stable isotopes of δ13C and δ15N to examine the fundamental characteristics of trophic position, trophic niche, and carbon source for the food web in the midstream of the Chishui River, a tributary to the Yangtze River. Our results showed that stable isotope signatures among different sorts of basal resources and consumers were significantly distinguishable and that the food chain consisted of four trophic levels, indicating the multiple trophic pathways and long food chain length here. The trophic guilds of fish were classified into four categories, in which herbivorous and carnivorous fish showed greater trophic diversity and omnivorous fish had higher trophic redundancy, which meant that there was a stable trophic niche structure in the study area. Phytoplankton and periphyton presented the largest contributions to consumers, indicating that autochthonous productivity was the dominant carbon source in the midstream of the Chishui River. Since the Chishui River is still in a natural condition without any dam constructions, the autochthonous productivity, stable trophic niche structure, multiple trophic pathways and long food chain length found here demonstrate its high conservation value. Therefore, the strategy to refrain from damming on this river should persist into the future. Full article
(This article belongs to the Section Biodiversity and Functionality of Aquatic Ecosystems)
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Figure 1

Figure 1
<p>Map of study area (dashed box) in the Chishui River basin (shaded part). Dotted lines represent the simplification of the river reaches.</p>
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<p>Stable isotope (δ<sup>13</sup>C and δ<sup>15</sup>N) signatures bi-plot for basal resources (green dots), invertebrates (red diamonds), and fishes (black triangles) in the midstream of the Chishui River.</p>
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<p>Hierarchical cluster analysis (Bray–Curtis similarity) and non-metric multidimensional scaling (NMDS) ordination based on δ<sup>13</sup>C and δ<sup>15</sup>N signatures for trophic guilds of fish in the midstream of the Chishui River. Guild I represents herbivores; Guild II represents herbivore-based omnivores; Guild III represents carnivore-based omnivores; Guild IV represents carnivores.</p>
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<p>Isotopic niche for trophic guilds of fish in the midstream of the Chishui River.</p>
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