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Diversity, Volume 16, Issue 4 (April 2024) – 62 articles

Cover Story (view full-size image): The karst areas of the Balkans are one of the world’s most important hotspots of subterranean biodiversity. This paper presents the results of a three-year study on the diversity of terrestrial arthropods in Resava Cave in eastern Serbia. To date, a total of 107 species of terrestrial arthropods (4 troglobitic, 16 troglophilic and 87 trogloxenic) have been found in the cave: 66 hexapods, 27 chelicerates, 11 myriapods and 3 crustaceans. The most significant inhabitants of the cave are certainly troglobitic species, including the completely blind and depigmented millipede Serbosoma kucajense (cover photo), a member of the genus Serbosoma, which is endemic to several caves and pits on the Kučajske Planine Mts. and Mt. Beljanica in eastern Serbia. View this paper
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10 pages, 1607 KiB  
Article
Associations between Epiphytic Orchids and Their Hosts and Future Perspectives of These in the Context of Global Warming
by Binu Timsina, Zuzana Münzbergová, Pavel Kindlmann, Bishnu Prasad Bhattarai, Bikram Shrestha, Bhakta B. Raskoti and Maan B. Rokaya
Diversity 2024, 16(4), 252; https://doi.org/10.3390/d16040252 - 22 Apr 2024
Viewed by 1684
Abstract
Epiphytic species are ecologically important and a significant component of biodiversity. To ensure their efficient conservation, we need to understand their ecology and host plant associations. It is also important to investigate how the predicted temperature change will affect their future distribution. Here, [...] Read more.
Epiphytic species are ecologically important and a significant component of biodiversity. To ensure their efficient conservation, we need to understand their ecology and host plant associations. It is also important to investigate how the predicted temperature change will affect their future distribution. Here, we use data collected in Nepal to investigate how epiphytic orchids are associated with host species, their distribution patterns, and how they may be threatened by the predicted increase in temperature towards the end of the 21st century. We used the phi coefficient (Φ) of association to calculate the associations of epiphytic orchid species with plants and rarefaction to describe the diversity of orchids associated with a particular host species. We used interpolation to estimate the distribution of epiphytic orchids and their host species along altitudinal gradients. The phi (Φ) coefficient of association revealed that 30 species of host plants showed more association with different orchid species than expected. The number of epiphytic orchids increased with the number of host individuals. We predict that an increase in temperature by ~3 °C, which is a more moderate value of temperature increase by the end of the 21st century, will affect at least 52 narrow-ranged species of orchids and 58 narrow-ranged species of host plants. Therefore, we should make efforts to prevent many plant species from becoming extinct, as an increase in temperature is likely to affect their existence. Full article
(This article belongs to the Section Biogeography and Macroecology)
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<p>The number of orchid species occurring more frequently than expected by chance in a given host species with the phi coefficient (Φ) &gt; 0.2 for the data obtained in Nepal, 2006–2011.</p>
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<p>The number of orchid species found on each host species was limited to 20 individuals sampled, as there was a sufficient number of orchid individuals for resample analysis found in all the host species for the data obtained in Nepal in 2006–2011.</p>
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<p>Relationship between the total number of orchid species and host species recorded from 2006–2011. Each dot represents the number of orchid species (log + 1) per host individual of a particular species (log) in each region for the obtained data.</p>
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<p>Relationship between host species and epiphytic orchids along altitudinal gradients recorded in the study in Nepal, 2006–2011. Each dot represents the species richness of host or orchid species at respective altitudes.</p>
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<p>Relationship between the projected moderate increase in temperature by the year 2100 and the numbers of host plant species and epiphytic orchid species that will be affected in Nepal for the data obtained from 2006 to 2011.</p>
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27 pages, 3827 KiB  
Review
Management Strategies of Prosopis juliflora in Eastern Africa: What Works Where?
by Hellen Wangechi Kamiri, Simon K. Choge and Mathias Becker
Diversity 2024, 16(4), 251; https://doi.org/10.3390/d16040251 - 22 Apr 2024
Cited by 2 | Viewed by 2019
Abstract
Prosopis juliflora is a shrub/tree originating from the Americas. Since its introduction for fuel wood afforestation into eastern Africa, it has been invading crop- and rangelands with negative effects on the environment and on livelihoods. Understanding the management strategies for Prosopis and matching [...] Read more.
Prosopis juliflora is a shrub/tree originating from the Americas. Since its introduction for fuel wood afforestation into eastern Africa, it has been invading crop- and rangelands with negative effects on the environment and on livelihoods. Understanding the management strategies for Prosopis and matching them with ecological, social-cultural, and economic needs of the eastern African region is a pressing scientific issue. We analyzed management strategies of Prosopis, focusing on determinants and drivers of their choice of applied management strategies as well as their effectiveness. We identified 1917 scientific contributions published between 1970 and 2022. Following a multi-step screening, we reduced the references to 53 relevant (internationally) published papers with a focus on the management of Prosopis in the east African region. Analysis of the literature shows that factors driving invasion dynamics but also land users’ social-economic as well as cultural attributes determine the type of management strategy and shape local control actions. Main strategies comprise (1) physical containment of invasive spread, (2) chemical, mechanical and biological approaches to reduce stand densities, (3) complete eradication, (4) restoration of invaded land, and (5) economic use of Prosopis products. Adopted strategies are based on actual and perceived impacts of invasion, and the adoption and success of individual strategies is highly location specific. Full article
(This article belongs to the Special Issue Ecology and Evolution of Invasive Plant Species)
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<p>Overview maps showing the eastern Africa countries concerned in the reviewed studies on management strategies of <span class="html-italic">Prosopis</span>. The regions marked in red perimeter namely Kasalla in Sudan (<b>A</b>); Hargeisa in Somalia (<b>B</b>); Afar in Ethiopia (<b>C</b>); Arusha, Kilimanjaro, and Manyara in Tanzania (<b>D</b>); and Baringo, Turkana, and Bura in Kenya (<b>E</b>) are the major areas of <span class="html-italic">Prosopis</span> infestation.</p>
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<p>Flow chart detailing the process of screening and identifying references for their eligibility to be included in the systematic review of management of <span class="html-italic">Prosopis</span> in eastern Africa. The solid line represents different phases of the systematic review while broken lines represent steps leading to additional or exclusion of papers. (adapted from [<a href="#B74-diversity-16-00251" class="html-bibr">74</a>]).</p>
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<p>(<b>a</b>) Countries in eastern Africa where studies on management of <span class="html-italic">Prosopis</span> has been reported (here, share of published papers per country), while (<b>b</b>) shows the share of the type of management strategies for <span class="html-italic">Prosopis</span> applied in the reported studies (<span class="html-italic">n</span> = 59 citations).</p>
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<p>Hypothesized pathways, including drivers and pressures of invasive spread, as well as impacts and response strategies to an invasion by <span class="html-italic">Prosopis</span>, following the DPSIR framework [<a href="#B110-diversity-16-00251" class="html-bibr">110</a>].</p>
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10 pages, 5616 KiB  
Article
Types and Fecundity of Neotenic Reproductives Produced in 5-Year-Old Orphaned Colonies of the Drywood Termite, Cryptotermes domesticus (Blattodea: Kalotermitidae)
by Wenjing Wu, Zhenyou Huang, Shijun Zhang, Zhiqiang Li, Bingrong Liu, Wenhui Zeng and Chuanguo Xia
Diversity 2024, 16(4), 250; https://doi.org/10.3390/d16040250 - 22 Apr 2024
Viewed by 941
Abstract
Orphaned colonies of Cryptotermes domesticus readily produce replacement reproductives and continue propagation. In this study, we aimed to investigate the production and fecundity of neotenic reproductives in 5-year-old colonies of C. domesticus after orphaning. All 15 experimental colonies were successfully re-established by the [...] Read more.
Orphaned colonies of Cryptotermes domesticus readily produce replacement reproductives and continue propagation. In this study, we aimed to investigate the production and fecundity of neotenic reproductives in 5-year-old colonies of C. domesticus after orphaning. All 15 experimental colonies were successfully re-established by the neotenic reproductive pair. Three types of neotenic reproductives with various wing-bud lengths were observed: type I with micro wing buds, type II with short wing buds, and type III with long wing buds. Four patterns of pairs made up of these neotenics, namely, type I + type II, type I + type III, type II + type II, and type II + type III, exhibited reproductive capacities similar to those of the primary reproductive pair. We speculated that these neotenic reproductives were derived from various nymphal instars. The 5-year-old colonies had three instars of nymphs, with the majority being in the second instar, followed by the first. Thus, the combination of neotenic reproductives with short wing buds and micro wing buds was the dominant differentiation pathway of the orphaned colonies. After the removal of the original primary reproductive pair, the nymphs matured into neotenic reproductives and took over reproduction in the colony in 107.40 ± 15.18 days. This study highlights the importance of quarantine and routine inspection of wood, as well as the significance of early prevention and control of C. domesticus infestation in wood. Moreover, this study confirms the high differentiation and reproductive capacities of C. domesticus. Full article
(This article belongs to the Special Issue Diversity and Ecology of Termites)
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<p>The emergence time of the first neotenic, second neotenic, first egg, and first larva in each experimental colony of <span class="html-italic">Cryptotermes domesticus</span>.</p>
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<p>Colonies established by (<b>A</b>) primary reproductives and (<b>B</b>) neotenic reproductives of <span class="html-italic">Cryptotermes domesticus</span>.</p>
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<p>Types of neotenic reproductives of <span class="html-italic">Cryptotermes domesticus</span> with different wing-bud lengths: (<b>A</b>) Type I with micro wing buds. (<b>B</b>) Type II with short wing buds. (<b>C</b>) Type III with long wing buds. The red arrows indicate the wing buds. The schematic diagrams of the wing buds are provided below the photographs.</p>
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<p>The numbers of eggs and larvae one year after colony re-establishment of <span class="html-italic">Cryptotermes domesticus</span>.</p>
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14 pages, 3332 KiB  
Article
Soil-Microbial CNP Content and Ecological Stoichiometry Characteristics of Typical Broad-Leaved Tree Communities in Fanjing Mountain in Spring
by Wenmin Luo, Xianliang Wu, Sheng Chen, Guiting Mu and Yingying Liu
Diversity 2024, 16(4), 249; https://doi.org/10.3390/d16040249 - 22 Apr 2024
Viewed by 928
Abstract
This study aims to investigate the impact of diverse forest stand types and soil depths on soil ecological stoichiometry characteristics, shedding light on nutrient limitations and cycling patterns within the mid-subtropical forest ecosystem in southwest China during spring. The research focused on four [...] Read more.
This study aims to investigate the impact of diverse forest stand types and soil depths on soil ecological stoichiometry characteristics, shedding light on nutrient limitations and cycling patterns within the mid-subtropical forest ecosystem in southwest China during spring. The research focused on four representative forest stands situated in Fanjing Mountain: Castanopsis fargesii (C. fargesii), Cyclobalanopsis multiervis (C. multiervis), Cyclobalanopsis argyrotricha (C. argyrotricha), and Rhododendron argyrophyllum Franch (R. argyrophyllum). Sample plots were established in these forest types, and soil samples were collected from the 0–20 cm and 20–40 cm soil layers in March, spring of 2023. Various soil parameters, including pH, soil organic carbon (SOC), total nitrogen (TN), total phosphorus (TP), soil microbial biomass carbon (MBC), soil microbial nitrogen (MBN), and soil microbial phosphorus (MBP) were measured, and their stoichiometric ratios were calculated. The findings of the study were as follows: (1) In the 0–20 cm soil layer, C. argyrotricha exhibited the highest soil organic carbon, followed by C. fargesii, C. multiervis, and R. argyrophyllum with the lowest content. No significant differences in soil organic carbon were observed among the four forests in the 20–40 cm soil layer. Additionally, C. argyrotricha displayed a significantly higher soil C:N ratio compared to other forest types in different soil layers. In the typical broad-leaved forest area of Fanjing Mountain, the TP was classified as deficient. (2) In the 0–20 cm soil layer, the MBC of C. fargesii surpassed C. multiervis, C. argyrotricha, and R. argyrophyllum by 26.59%, 42.92%, and 24.67%, respectively. There were no significant differences in soil MBC:MBP ratio and MBN:MBP ratio, regardless of forest species and soil depths. The low availability of soil nitrogen in different forest stand types in Fanjing Mountain strongly limits soil microorganism biomass. (3) The correlation between SOC, TN, TP, and their stoichiometric ratios varied across different soil layers. Therefore, in managing the Fanjing Mountain forest area, attention should be paid to supplementing N and P in the soil. Full article
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<p>Location of the study area in Mount Fanjing. Ⅰ, <span class="html-italic">C. fargesii</span>; Ⅱ, <span class="html-italic">C. multiervis</span>; Ⅲ, <span class="html-italic">C. argyrotricha</span>; Ⅳ, <span class="html-italic">R. argyrophyllum</span>.</p>
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<p>SOC, TN, and TP stoichiometric indexes of 0–20 cm and 20–40 cm soil layers in four forest types. Ⅰ, <span class="html-italic">C. fargesii</span>; Ⅱ, <span class="html-italic">C. multiervis</span>; Ⅲ, <span class="html-italic">C. argyrotricha</span>; Ⅳ, <span class="html-italic">R. argyrophyllum</span>. A of X-axis, 0–20 cm soil layer; B of X-axis, 20–40 cm soil layer. Subfigure (<b>A</b>), content of SOC; subfigure (<b>B</b>), content of TN; subfigure (<b>C</b>), content of TP; subfigure (<b>D</b>), ratio of C:N; subfigure (<b>E</b>), ratio of C:P; subfigure (<b>F</b>), ratio of N:P. Different lowercase letters indicate significant differences at <span class="html-italic">p</span> &lt; 0.05 among the 20–40 cm soil layer in four forest types; different uppercase letters indicate significant differences at <span class="html-italic">p</span> &lt; 0.05 among the 0–20 cm soil layer in four forest types. * indicates significant differences between the 0–20 cm soil layer and 20–40 cm soil layer at the same forest type (<span class="html-italic">p</span> &lt; 0.05).</p>
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<p>Carbon, nitrogen, and phosphorus stoichiometric indexes of the microbial biomass of the 0–20 cm and 20–40 cm soil layers in four different forest types. Ⅰ, <span class="html-italic">C. fargesii</span>; Ⅱ, <span class="html-italic">C. multiervis</span>; Ⅲ, <span class="html-italic">C. argyrotricha</span>; Ⅳ, <span class="html-italic">R. argyrophyllum</span>. A of X-axis, 0–20 cm soil layer; B of X-axis, 20–40 cm soil layer. Subfigure (<b>A</b>), content of MBC; subfigure (<b>B</b>), content of MBN; subfigure (<b>C</b>), content of MBP; subfigure (<b>D</b>), ratio of MBC:MBN; subfigure (<b>E</b>), ratio of MBC:MBP; subfigure (<b>F</b>), ratio of MBN:MBP. Different lowercase letters indicate significant differences at <span class="html-italic">p</span> &lt; 0.05 among the 20–40 cm soil layers in four forest types. Different uppercase letters indicate significant differences at <span class="html-italic">p</span> &lt; 0.05 among 0–20 cm soil layers in four forest types. * indicates significant differences between the 0–20 cm soil layer and 20–40 cm soil layer within the same forest type at <span class="html-italic">p</span> &lt; 0.05.</p>
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<p>Pearson’s correlation heatmap of between soil microbial biomass carbon, nitrogen, and phosphorus and its ecostoichiometric ratio in the 0–20 cm soil layer (<b>A</b>) and 20–40 cm soil layer (<b>B</b>). Note: * represents significant difference at 0.05 level; ** represents significant difference at 0.01 level; the number axis represents the magnitude of the correlation coefficient value, where red denotes a positive correlation and blue denotes a negative correlation.</p>
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<p>Biplots of redundancy analysis. Note: Biplots of redundancy analysis to show associations between environmental variables and C:N:P ecological stoichiometry in soil and microbial biomass of 0–20 cm (<b>A</b>) and between environmental variables and C:N:P ecological stoichiometry in soil and microbial biomass of 20–40 cm (<b>B</b>). Arrows pointing in the same direction indicate variables that are positively correlated, whereas arrows pointing in opposite directions indicate variables that are negatively correlated. Abbreviations: FT, forest type; SWF, water accommodated fraction; AT, altitude; AS, aspect; SL, slope; SOC, soil organic carbon; TN, total nitrogen; TP, total phosphorus; MBC, microbial biomass C; MBN, microbial biomass N; MBP, microbial biomass P.</p>
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16 pages, 80710 KiB  
Article
Phylogenetic Trends in the Dissymmetrisation of Genitalia in Hadenini (Lepidoptera, Noctuidae)
by Zoltán Varga, Gábor Ronkay and László Ronkay
Diversity 2024, 16(4), 248; https://doi.org/10.3390/d16040248 - 22 Apr 2024
Viewed by 1141
Abstract
The external genital appendages of Noctuidae represent correlated–coevolved elements of a complex structure. The pathways of changes are delimited by some constraints, and they are parallelly evolved in different phyletic lines. Asymmetrical male external genitalia were found in Hadenini, in Polia and its [...] Read more.
The external genital appendages of Noctuidae represent correlated–coevolved elements of a complex structure. The pathways of changes are delimited by some constraints, and they are parallelly evolved in different phyletic lines. Asymmetrical male external genitalia were found in Hadenini, in Polia and its closely related genera, but also in Anarta (s. l.). In Poliina, the asymmetry of the genital capsule is mostly expressed in the Holarctic Polia nebulosa species group, forming the basal split within Polia (s. str.). Higher species diversity, as a consequence of asymmetry connected with the split of functions between the right and left sides, was observed in Polia (s. str.) and in Anarta (s. l.). The highest level of expansivity was observed in the Holarctic Anarta, where some species are migrating and becoming invasive ones, while a bulk of species populates the steppic and mountainous habitats of North America and Central Asia. Parallelly, while some genera/subgenera of the subtribe Poliina are oligotypic and/or consist of strictly localised species, the sensu stricto Polia species with asymmetrical genital capsules are widely distributed. The diversification of the Hadulina phylogenetic line should have been initiated by the Messinian aridisation crisis. The core area of diversification of Poliina was connected with the Sino-Himalayan region, followed by expansion into the Holarctic boreo-nemoral zone. Full article
(This article belongs to the Special Issue Speciation, Phylogenetics and Taxonomy of Lepidoptera)
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<p>Examples of symmetrical vs. asymmetrical genital capsules. (<b>A</b>) <span class="html-italic">Haderonia arschanica</span> with reduced saccular processes; (<b>B</b>) <span class="html-italic">Polia</span> (<span class="html-italic">Metallopolia</span>) <span class="html-italic">kalikotei</span> with short, symmetrical saccular processes and slightly asymmetrical setae; (<b>C</b>) <span class="html-italic">Polia</span> (<span class="html-italic">Polia</span>) <span class="html-italic">nebulosa</span> with strongly asymmetrical saccular processes and differentiated groups of setae (males).</p>
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<p>Four different genera/subgenera of Poliina with nearly completely symmetrical genital capsules: (<b>A</b>) <span class="html-italic">Haderonia miserabilis</span>; (<b>B</b>) <span class="html-italic">Ctenoceratoda sukharevae</span>; (<b>C</b>) <span class="html-italic">Tricheurois retrusa</span>; and (<b>D</b>) <span class="html-italic">Polia</span> (<span class="html-italic">Protopolia</span>) <span class="html-italic">praecipua</span> (males).</p>
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<p>(<b>A</b>) <span class="html-italic">Polia</span> (<span class="html-italic">Metallopolia</span>) <span class="html-italic">culta</span>; (<b>C</b>) <span class="html-italic">Polia</span> (<span class="html-italic">Metallopolia</span>) <span class="html-italic">dysgnorima</span>; (<b>B</b>) <span class="html-italic">Polia</span> (<span class="html-italic">Metallopolia</span>) <span class="html-italic">kisculta</span>; and (<b>D</b>) <span class="html-italic">Polia</span> (<span class="html-italic">Metallopolia</span>) <span class="html-italic">metagnorima</span> (males). Himalayan (<b>A</b>,<b>B</b>) vs. West China (<b>C</b>,<b>D</b>) allopatric pairs of species.</p>
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<p>(<b>A</b>) <span class="html-italic">Polia</span> (<span class="html-italic">Polia</span>) <span class="html-italic">vesperugo</span>; (<b>B</b>) <span class="html-italic">Polia</span> (<span class="html-italic">Polia</span>) <span class="html-italic">propodea</span>. Genital capsules of Palearctic vs. Nearctic Boreal sister species.</p>
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<p>(<b>A</b>) <span class="html-italic">Polia</span> (<span class="html-italic">Polia</span>) <span class="html-italic">gigantea</span>; (<b>B</b>) <span class="html-italic">Polia</span> (<span class="html-italic">Polia</span>) <span class="html-italic">piniae</span>. Genital capsules displaying extreme dissymmetry in <span class="html-italic">Polia nebulosa</span> group.</p>
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<p>(<b>A</b>) <span class="html-italic">Polia</span> (<span class="html-italic">Polia</span>) <span class="html-italic">griseifusa</span>; (<b>B</b>) <span class="html-italic">Polia</span> (<span class="html-italic">Leuconephropolia</span>) <span class="html-italic">albirena</span>. Genital capsules illustrating taxonomically isolated species with symmetrical structures.</p>
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<p>(<b>A</b>) <span class="html-italic">Polia</span> (<span class="html-italic">Polia</span>) <span class="html-italic">serratilinea serratilinea</span>; (<b>B</b>) <span class="html-italic">Polia</span> (<span class="html-italic">Polia</span>) <span class="html-italic">serratilinea spalax</span>. Genital capsules—case of dissymmetry in saccular processes (allopatric subspecies).</p>
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<p>(<b>A</b>) <span class="html-italic">Odontelia arenicola</span>; (<b>B</b>) <span class="html-italic">Thargelia gigantea</span>. Genital capsules—cases of nearly symmetrical vs. strongly dissymmetrical structures in Discestrina.</p>
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<p>(<b>A</b>) <span class="html-italic">Anarta</span> (<span class="html-italic">Calocestra</span>) <span class="html-italic">farnhami palaearctica</span>; (<b>B</b>) <span class="html-italic">Anarta</span> (<span class="html-italic">Hadula</span>) <span class="html-italic">sabulorum</span>; (<b>C</b>) <span class="html-italic">Anarta</span> (<span class="html-italic">Calocestra</span>) <span class="html-italic">mendica</span>; and (<b>D</b>) <span class="html-italic">Anarta</span> (<span class="html-italic">Hadula</span>) <span class="html-italic">halodeserti</span> (males). A + C vs. B + D—two phyletic lines of dissymmetrisation in <span class="html-italic">Anarta</span> (s. l.).</p>
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<p>(<b>A</b>) <span class="html-italic">Cardiestra gobideserti</span>; (<b>B</b>) <span class="html-italic">Cardepia sociabilis deserticola</span>—cases of nearly symmetrical genital capsules in Discestrina.</p>
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<p>(<b>A</b>) <span class="html-italic">Thargelia distincta</span>; (<b>B</b>) <span class="html-italic">Thargelia leucostigma</span>—cases of strongly dissymmetrical genital capsules in Discestrina.</p>
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<p>(<b>A</b>) <span class="html-italic">Polia</span> (<span class="html-italic">Metallopolia</span>) <span class="html-italic">metagnorima</span>; (<b>B</b>) <span class="html-italic">Polia</span> (<span class="html-italic">Polia</span>) <span class="html-italic">malchani</span> (females)—the tubular shape of appendix bursae (<b>A</b>) corresponds with the elongate tubular endophallus, the short appendix bursae (<b>B</b>) with the simplified endophallus of males.</p>
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<p>(<b>A</b>) <span class="html-italic">Tricheurois landryi</span>; (<b>B</b>) <span class="html-italic">Ctenoceratoda tancrei</span> (females)—the tubular shape of the appendix bursae corresponds with the elongate tubular endophallus with fasciculate cornuti in males.</p>
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<p>(<b>A</b>) <span class="html-italic">Anarta</span> (<span class="html-italic">Hadula</span>) <span class="html-italic">insolita</span>; (<b>B</b>) <span class="html-italic">Anarta</span> (<span class="html-italic">Calocestra</span>) <span class="html-italic">schawyra</span> (females)—the appendix bursae is completely reduced in both phyletic lines of Discestrina.</p>
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<p>The sophisticated “lock-and-key” configuration of the corpus + appendix bursae vs. endophallus is a generic synapomorphy of the <span class="html-italic">Ctenoceratoda</span> species (<span class="html-italic">Ctenoceratoda tancrei</span>).</p>
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17 pages, 3001 KiB  
Article
Exploring the Influence of Soil Salinity on Microbiota Dynamics in Vitis vinifera cv. “Glera”: Insights into the Rhizosphere, Carposphere, and Yield Outcomes
by Andrea Colautti, Giovanni Mian, Diego Tomasi, Luke Bell and Patrick Marcuzzo
Diversity 2024, 16(4), 247; https://doi.org/10.3390/d16040247 - 20 Apr 2024
Cited by 1 | Viewed by 1562
Abstract
In a world grappling with the severe effects induced by climate change, one of the most significant concerns affecting agriculture is the gradual decline in water quality for irrigation associated with reduced rainfalls and the consequent increase in soil salinity. This issue is [...] Read more.
In a world grappling with the severe effects induced by climate change, one of the most significant concerns affecting agriculture is the gradual decline in water quality for irrigation associated with reduced rainfalls and the consequent increase in soil salinity. This issue is particularly crucial for grapevine cultivation (Vitis vinifera L.) and the associated winemaking industry. The aroma of the resulting wines and the yield parameters can be influenced both directly by water quality and indirectly due to the effects exerted by salinity on the microbiota, which directly impacts plant health. To gain insights into this topic, our study aimed to analyse the changes induced in the microbiota of both the rhizosphere and the carposphere due to salt stress using a metabarcoding approach, focusing on Vitis vinifera cv. Glera. The control plants were irrigated with rainwater, while the treated plants were irrigated with water containing salt (NaCl). Our findings revealed significant differences in the microbiota (both fungi and bacteria) of the rhizosphere and carposphere between the two treatments. For instance, the Shannon diversity index (i.e., alpha diversity) was lower in the treated plants compared to the control not-treated ones, whilst the beta diversity did not show any differences. Several microbial phyla exhibited better resilience to this abiotic stress (e.g., Ascomycota, Saccharomycetes, Acidobacteria, Proteobacteria, Bacteroidetes), shedding light on their impact on crucial bacterial and fungal groups essential for the subsequent winemaking stages. Additionally, the salt stress negatively affected the yield parameters. This study contributes valuable insights to the viticultural community, providing a deeper understanding of the complex interplay between soil characteristics, microbial communities, and their influence on productivity. Full article
(This article belongs to the Section Microbial Diversity and Culture Collections)
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<p>Graphic summary of the experimental design adopted in this work.</p>
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<p>Rhizosphere alpha diversity considering bacterial (<b>A</b>) and fungal (<b>B</b>) kingdoms; carposphere alpha diversity considering bacterial (<b>C</b>) and fungal (<b>D</b>) kingdoms.</p>
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<p>Rhizosphere beta diversity considering both bacterial (<b>A</b>) and fungal kingdoms (<b>B</b>).</p>
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<p>Carposphere beta diversity considering both bacterial (<b>A</b>) and fungal kingdoms (<b>B</b>).</p>
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<p>(<b>A</b>) Bacterial (16S) phyla above 0.5% identified in the plant rhizosphere of both control and treated plants; (<b>B</b>) fungal (ITS) phyla identified above 0.5% in the plant rhizosphere of both control and treated plants. Statistical analysis (<span class="html-italic">T</span> test) is reported (* <span class="html-italic">p</span> &lt; 0.05, ** <span class="html-italic">p</span> &lt; 0.01).</p>
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<p>(<b>A</b>) Bacterial (16S) classes identified above 0.5% in the plant carposphere of both control and treated plants; (<b>B</b>) fungal (ITS) classes identified above 0.5% in the plant carposphere of both control and treated plants. Statistical analysis (<span class="html-italic">T</span> test) is reported (* <span class="html-italic">p</span> &lt; 0.05, ** <span class="html-italic">p</span> &lt; 0.01).</p>
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<p>(<b>A</b>) Fifteen mains bacterial (16S) genera identified in the plant rhizosphere of both control and treated plants; (<b>B</b>) fifteen main fungal (ITS) genera identified in the plant rhizosphere of both control and treated plants. Statistical analysis (<span class="html-italic">T</span> test) is reported (* <span class="html-italic">p</span> &lt; 0.05, ** <span class="html-italic">p</span> &lt; 0.01).</p>
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15 pages, 6080 KiB  
Article
Ascochyta erotica sp. nov. Pathogenic on Convolvulus arvensis
by Maria Gomzhina and Elena Gasich
Diversity 2024, 16(4), 246; https://doi.org/10.3390/d16040246 - 20 Apr 2024
Viewed by 1046
Abstract
Convolvulus arvensis is an herbaceous dicotyledonous plant in the Convolvulaceae family that is native to Europe and Asia. It is a perennial soboliferous plant and is one of the most harmful weeds. This weed is successful in many types of climates, including temperate, [...] Read more.
Convolvulus arvensis is an herbaceous dicotyledonous plant in the Convolvulaceae family that is native to Europe and Asia. It is a perennial soboliferous plant and is one of the most harmful weeds. This weed is successful in many types of climates, including temperate, tropical, and Mediterranean climates, but it is most troublesome for agriculture throughout the temperate zone. In this study, several pathogenic isolates were collected from this host. The internal transcribed spacer (ITS) and large subunit (28S) or ribosomal DNA, partial DNA-directed RNA polymerase II subunit (rpb2), and β-tubulin (tub2) genes were amplified and sequenced for all the isolates studied. Further, both a multilocus phylogenetic analysis of DNA sequences and an analysis of morphological features were implemented. Based on the results obtained, all the studied isolates were found to be distinct from any described species in the genus Ascochyta and are, therefore, described here as a new species Ascochyta erotica sp. nov. The pathogenicity of A. erotica sp. nov. was also tested and confirmed on leaf segments of C. arvensis. Full article
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<p>Phylogenetic tree of <span class="html-italic">Ascochyta</span> species inferred from a maximum likelihood analysis based on a concatenated alignment of ITS, 28S, <span class="html-italic">rpb2</span>, and <span class="html-italic">tub2</span>. The maximum likelihood bootstrap support values (MLBS ≥ 70%), maximum parsimony bootstrap support values (MPBS ≥ 70%), and Bayesian posterior probabilities (BPP ≥ 0.70) are given at the nodes (MLBS/MPBS/BPP). Tree is rooted by <span class="html-italic">Phomatodes nebulosa</span> (CBS 117.93). The studied isolates are in blue, and the ex−type and representative strains are in bold.</p>
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<p><span class="html-italic">Ascochyta erotica</span> sp. nov. (ex-holotype culture MF-17.20). Colonies grown at different temperatures on various media after 10 days of growth. (<b>a</b>) PDA, 20 °C; (<b>b</b>) PDA, 25 °C; (<b>c</b>) PDA, 30 °C; (<b>d</b>) OA, 20 °C; (<b>e</b>) OA, 25 °C; (<b>f</b>) OA, 30 °C; (<b>g</b>) MEA, 20 °C; (<b>h</b>) MEA, 25 °C; (<b>i</b>) MEA, 30 °C.</p>
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<p><span class="html-italic">Ascochyta erotica</span> sp. nov. from the holotype material LEP 124536. (<b>a</b>) Necrotic lesions on <span class="html-italic">Convolvulus arvensis</span> leaf; (<b>b</b>) pycnidia on necrotic lesion; (<b>c</b>) conidia. Scale bars: (<b>b</b>) 1 mm; (<b>c</b>) 20 µm. Arrows indicate pycnidia.</p>
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<p><span class="html-italic">Ascochyta erotica</span> sp. nov. (ex-holotype culture MF-17.20). (<b>a</b>) Culture on PSA after 7 d of growth (front and reverse); (<b>b</b>) culture on OA after 7 d of growth (front and reverse); (<b>c</b>) culture on MEA after 7 d of growth (front and reverse); (<b>d</b>) culture on PSA after 14 d of growth (front and reverse); (<b>e</b>) culture on OA after 14 d of growth (front and reverse); (<b>f</b>) culture on MEA after 14 d of growth (front and reverse); (<b>g</b>–<b>k</b>) pycnidia from OA after 14 d of growth; (<b>l</b>) conidiogenous cells; (<b>m</b>) conidia. Scale bars: (<b>g</b>), 500 µm; (<b>h</b>,<b>i</b>), 100 µm; (<b>j</b>,<b>k</b>), 200 µm; (<b>l</b>,<b>m</b>), 20 µm.</p>
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<p>Pathogenicity of the <span class="html-italic">Ascochyta erotica</span> ex-type isolate MF-17.20 on leaf segments of <span class="html-italic">Convolvulus arvensis</span>. First line in each set (Petri dish) contains leaf segments inoculated with intact adaxial part; second line is adaxial part wounded with needle; third line is intact abaxial part; fourth line is abaxial part wounded with needle. Inoculation with mycelial suspension of isolate: (<b>a</b>) 3 days post treatment; (<b>b</b>) 7 days post treatment.</p>
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12 pages, 1568 KiB  
Article
Comparative Metagenomic Analysis of Marine eDNA Investigating the Production Crisis of Aquacultured Saccharina japonica
by Soyun Choi, Kwon Mo Yang, Dong Mun Choi, Yang Ho Choi, Xiuliang Wang, Lingxiu Wang, Xiaoyong Liu, Delin Duan, Hyun Park and Jeong Ha Kim
Diversity 2024, 16(4), 245; https://doi.org/10.3390/d16040245 - 19 Apr 2024
Viewed by 1171
Abstract
Aquaculture farms cultivating Saccharina japonica are highly active in Wando, Korea, and Rongcheng, China. However, the yield of S. japonica significantly declined in the Rongcheng region in 2022 compared to previous records, whereas that in Wando remained at a normal level, presumably due [...] Read more.
Aquaculture farms cultivating Saccharina japonica are highly active in Wando, Korea, and Rongcheng, China. However, the yield of S. japonica significantly declined in the Rongcheng region in 2022 compared to previous records, whereas that in Wando remained at a normal level, presumably due to the presence of a pathogenic microbiome. We used environmental DNA (eDNA) metagenomic analysis to compare the microbial compositions of seawater from aquaculture farms in Wando and Rongcheng. Seawater samples were collected from one Korean site in Wando (WA) and two Chinese sites in Ailian Bay (AB) and Lidao Bay (LB). Metagenomic analysis focusing on the microbial 16S rRNA identified 38 phyla and 58 families of microbiomes in all regions. Potentially pathogenic bacterial groups associated with S. japonica in AB and LB were more abundant than in WA, suggesting their potential influence on mortality and the decline in the harvest yield of S. japonica. The microbial composition of WA was distinguished from those of the other two sites, which clustered together with higher similarity. Since the S. japonica aquaculture industry is important for both countries, this comparative eDNA monitoring is a valuable initiation towards the next step of problem-solving practices in coastal management in these two aquaculture systems. Full article
(This article belongs to the Special Issue Microbial Diversity in Aquatic Systems)
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<p>Sampling sites of seawater samples of Korea and China: Bogil-do: Wando, Korea (WA); Ailian Bay, Rongcheng China (AB); Lidao Bay, Rongcheng China (LB).</p>
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<p>Taxonomic microbial composition and relative abundance at (<b>a</b>) phylum and (<b>b</b>) family level in each seawater sample. (<b>c</b>) Heatmap legend shows the ratio of the tentative pathogenic bacteria in genus level relative to the total counts in AB, LB, and WA. Four major tentatively pathogenic bacteria, <span class="html-italic">Pseudoalteromonas</span>, <span class="html-italic">Vibrio</span>, <span class="html-italic">Pseudomonas</span>, and <span class="html-italic">Sulfitobacter,</span> were more abundant in the China seawater samples, AB and LB.</p>
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<p>(<b>a</b>) Comparison of the alpha diversity values between three regions. WA showed the highest microbial diversity and generally high microbial evenness with AB. LB showed the lowest microbial diversity and evenness. (<b>b</b>) PCoA results based on Jaccard distance performed at OTU level of AB, LB, and WA. Three regions were separated from each other, but clustered into Korea and China groups. (<b>c</b>) UPGMA Tree based on Jaccard distance combined with microbial composition and relative abundance of top 10 phyla in AB, LB, and WA. (<b>d</b>) Venn diagram representing the distribution of OTU numbers among AB, LB, and WA.</p>
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20 pages, 7639 KiB  
Article
Ecological Impacts of Introduced European Rabbits (Oryctolagus cuniculus) on Island Ecosystems in the Mediterranean
by Angelina Kossoff, Sheila Schueller, Hannah Nossan, Ian Slack, Pavlos Avramidis and Johannes Foufopoulos
Diversity 2024, 16(4), 244; https://doi.org/10.3390/d16040244 - 19 Apr 2024
Cited by 1 | Viewed by 1441
Abstract
The Cyclades Islands (Aegean Sea, Greece) are part of the Mediterranean Basin biodiversity hotspot and harbor a plethora of endemic species. Plant communities on the smaller islands in this region have largely evolved in the absence of herbivory and frequently lack antiherbivore defenses. [...] Read more.
The Cyclades Islands (Aegean Sea, Greece) are part of the Mediterranean Basin biodiversity hotspot and harbor a plethora of endemic species. Plant communities on the smaller islands in this region have largely evolved in the absence of herbivory and frequently lack antiherbivore defenses. This study evaluates the short- and long-term effects of the European rabbit (Oryctolagus cuniculus), an herbivore that has been released on numerous islands in the region, by comparing islands that 1. have historically been rabbit-free (ungrazed); 2. are currently grazed by rabbits, and 3. have previously been grazed, but are now rabbit-free. Ecological impacts of rabbits on the Aegean Islands were investigated by assessing the abundance, composition, and diversity of plant and arthropod communities as well as soil characteristics. Our results indicate that ungrazed islands have more arthropod species, more specialized or endemic plant species, and less exposed soil than currently grazed islands. While ungrazed islands did not necessarily possess higher total plant species richness, they did harbor significantly more small-island endemic taxa relative to presently grazed islands. This study indicates that native plant communities on Mediterranean islets are not adapted to the presence of this introduced species and that the practice of intentionally releasing rabbits on islands has significant and lasting negative ecological impacts, especially on small islands. While a complete recovery of post-rabbit was not evident over the time span of our research, both arthropod and plant data indicate that partial recovery is possible once rabbits have been removed. Full article
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<p>Map of study sites, with brown indicating islands that are currently being grazed by rabbits, green indicating islands that have never been grazed, and yellow representing islands with eradicated rabbit populations.</p>
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<p>Rabbit introductions have been an increasingly widespread phenomenon on Aegean Sea islands [<a href="#B32-diversity-16-00244" class="html-bibr">32</a>]. The above map shows the islands in the Cyclades with documented introduced European rabbit populations. Satellite islands (denoted in red) are likely to harbor floras with small island specialists and, therefore, more likely to be impacted by rabbits. Larger islands (denoted in orange) are inhabited by humans and livestock and have plant species communities largely adapted to herbivory. Islands are listed in <a href="#diversity-16-00244-t0A2" class="html-table">Table A2</a> in the <a href="#app1-diversity-16-00244" class="html-app">Appendix A</a>.</p>
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<p>Changes in the percent of bush, herbaceous vegetation, bare soil, and exposed rock cover across the three types of grazing categories. Dark green represents bush cover; light green represents herbaceous cover; brown represents soil cover, and gray represents rock cover. Significant differences (<span class="html-italic">p</span> &lt; 0.05) are denoted by *.</p>
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<p>Relationship between vegetation height (cm) and percent vegetation cover on the study islands, shown separately for each category of rabbit grazing status.</p>
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<p>Total number of specialist/endemic plant species across the three different grazing statuses. Islands with rabbits had significantly fewer such plant species relative to ungrazed islands.</p>
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<p>Differences in abundance of arthropods per pitfall trap on the study islands (corrected for island area).</p>
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<p>Boxplot of soil depth with individual data points overlaid across the three island categories.</p>
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<p>Endemic plant taxa found on Aegean Islets that are vulnerable to impacts from grazing. (<b>A</b>) <span class="html-italic">Campanula heterophylla</span> (JF). (<b>B</b>) <span class="html-italic">Dianthus fruticosus</span> (JF). (<b>C</b>) <span class="html-italic">Scorzonera araneosa</span> (JF). (<b>D</b>) <span class="html-italic">Brassica cretica</span> (JF). (<b>E</b>) <span class="html-italic">Origanum calcaratum</span> (<span class="html-italic">G. Gavalas</span>). (<b>F</b>) <span class="html-italic">Helichrysum amorginum</span> (JF).</p>
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<p>Photographs of some of our study islands across the three rabbit presence categories. Images show how rabbits mainly target low, herbaceous vegetation and less woody perennial species (e.g., <span class="html-italic">Pistacea lentiscus</span>) that often remain unaffected by rabbits due to their chemical and physical defenses or height. Post-rabbit islands are characterized primarily by the re-colonization of areas between these scrubby perennials by low annuals. However, any such recovery never attains the original, ungrazed levels of vegetation cover, at least not without additional restoration steps. Images from Angelina Kossoff, 2022, and Agia Kali from Johannes Foufopoulos, 2022.</p>
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<p>Box plot displaying the variation in vegetation height (cm) across the three island classifications. Individual data points are overlaid across the boxplots.</p>
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18 pages, 8066 KiB  
Article
Taxonomic Insights into Caulerpa (Bryopsidales, Chlorophyta) Species in French Polynesia: Confirmation of 13 Species and Reinstatement of C. pickeringii Harvey & Bailey
by Laura Lagourgue, Thomas Sauvage, Mayalen Zubia, Stefano G. A. Draisma, Christophe Vieira, Aschwin Engelen and Claude E. Payri
Diversity 2024, 16(4), 243; https://doi.org/10.3390/d16040243 - 18 Apr 2024
Viewed by 1476
Abstract
Caulerpa J.V. Lamouroux is a genus of green macroalgae belonging to the family Caulerpaceae in the order Bryopsidales. The genus comprises 104 currently accepted species, of which 51 have been recorded from Pacific Islands. Among these islands, French Polynesia is found in the [...] Read more.
Caulerpa J.V. Lamouroux is a genus of green macroalgae belonging to the family Caulerpaceae in the order Bryopsidales. The genus comprises 104 currently accepted species, of which 51 have been recorded from Pacific Islands. Among these islands, French Polynesia is found in the middle of the South Pacific Ocean and includes five archipelagos (i.e., the Austral, Gambier, Marquesas, Society, and Tuamotu Islands) where seaweed inventories have reported a total of 16 Caulerpa species so far based on morphology. Here, based on a sampling covering the five archipelagos of French Polynesia, we attempt to (i) verify the taxonomy of Caulerpa species present in these regions based on phylogeny, (ii) describe in more detail the specific diversity between the five archipelagos, and (iii) provide a morphological identification tool for these species. We successfully obtained 134 new tufA sequences for phylogenetic analyses, which corresponded to 13 species. We propose to resurrect C. pickeringii Harvey & Bailey for representatives of C. webbiana var. pickeringii and classify it in the Caulerpa subgenus Araucarioideae. We also transfer C. seuratii to C. pickeringii based on genetic results. A new morphological identification key is provided as well as an updated distribution of Caulerpa species across French Polynesia. Full article
(This article belongs to the Special Issue Diversity in 2024)
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<p>(<b>A</b>): Position of Tuvalu islands (<b>left</b>) and French Polynesia archipelagos (<b>right</b>) in the Pacific Ocean (source: TUBS from CC BY-SA 3.0, <a href="https://commons.wikimedia.org/wiki/Main_Page" target="_blank">https://commons.wikimedia.org/wiki/Main_Page</a>, accessed on 25 January 2024); (<b>B</b>): Distribution maps of samples from French Polynesia used in this study, with a zoom to the five archipelagos. Red dots are samples successfully sequenced, blue dots are specimens for which DNA was not available, and green triangles are samples from GenBank, including specimens from [<a href="#B13-diversity-16-00243" class="html-bibr">13</a>].</p>
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<p>ML phylogeny of <span class="html-italic">Caulerpa</span> species for the <span class="html-italic">tuf</span>A gene. Geographic origin of sequences integrated in the phylogeny are indicated at the country level, and at sub-level when relevant. The species presented in French Polynesia and Tuvalu are highlighted in blue and sample localities are indicated in bold. ML bs/BI PP values are reported at nodes if &gt;50% and &gt;0.50, respectively. Abbreviations: FP: French Polynesia, NSW: New South Wales (Australia), USA: United States of America. Example images by Claude Payri, Mayalen Zubia, Orempuller J., and Menou Jean-Louis. (<b>a</b>): first part: <span class="html-italic">Caulerpa</span> subgenera <span class="html-italic">Cliftonii</span>, <span class="html-italic">Hedleyi</span>, <span class="html-italic">Araucarioideae</span>, <span class="html-italic">Caulerpella</span>, and <span class="html-italic">Charoideae</span> and subgenus <span class="html-italic">Caulerpa</span> section <span class="html-italic">Sedoideae</span> and part of section <span class="html-italic">Caulerpa</span> (see <b>b</b>,<b>c</b> for detail of the prune clade). (<b>b</b>): second part: Subgenus <span class="html-italic">Caulerpa</span>, section <span class="html-italic">Caulerpa</span> (see <b>a</b>,<b>c</b> for detail of the prune clade). (<b>c</b>): third part: Subgenus <span class="html-italic">Caulerpa</span>, section <span class="html-italic">Caulerpa</span> (see <b>a</b>,<b>b</b> for detail of the prune clades).</p>
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<p>ML phylogeny of <span class="html-italic">Caulerpa</span> species for the <span class="html-italic">tuf</span>A gene. Geographic origin of sequences integrated in the phylogeny are indicated at the country level, and at sub-level when relevant. The species presented in French Polynesia and Tuvalu are highlighted in blue and sample localities are indicated in bold. ML bs/BI PP values are reported at nodes if &gt;50% and &gt;0.50, respectively. Abbreviations: FP: French Polynesia, NSW: New South Wales (Australia), USA: United States of America. Example images by Claude Payri, Mayalen Zubia, Orempuller J., and Menou Jean-Louis. (<b>a</b>): first part: <span class="html-italic">Caulerpa</span> subgenera <span class="html-italic">Cliftonii</span>, <span class="html-italic">Hedleyi</span>, <span class="html-italic">Araucarioideae</span>, <span class="html-italic">Caulerpella</span>, and <span class="html-italic">Charoideae</span> and subgenus <span class="html-italic">Caulerpa</span> section <span class="html-italic">Sedoideae</span> and part of section <span class="html-italic">Caulerpa</span> (see <b>b</b>,<b>c</b> for detail of the prune clade). (<b>b</b>): second part: Subgenus <span class="html-italic">Caulerpa</span>, section <span class="html-italic">Caulerpa</span> (see <b>a</b>,<b>c</b> for detail of the prune clade). (<b>c</b>): third part: Subgenus <span class="html-italic">Caulerpa</span>, section <span class="html-italic">Caulerpa</span> (see <b>a</b>,<b>b</b> for detail of the prune clades).</p>
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<p>ML phylogeny of <span class="html-italic">Caulerpa</span> species for the <span class="html-italic">tuf</span>A gene. Geographic origin of sequences integrated in the phylogeny are indicated at the country level, and at sub-level when relevant. The species presented in French Polynesia and Tuvalu are highlighted in blue and sample localities are indicated in bold. ML bs/BI PP values are reported at nodes if &gt;50% and &gt;0.50, respectively. Abbreviations: FP: French Polynesia, NSW: New South Wales (Australia), USA: United States of America. Example images by Claude Payri, Mayalen Zubia, Orempuller J., and Menou Jean-Louis. (<b>a</b>): first part: <span class="html-italic">Caulerpa</span> subgenera <span class="html-italic">Cliftonii</span>, <span class="html-italic">Hedleyi</span>, <span class="html-italic">Araucarioideae</span>, <span class="html-italic">Caulerpella</span>, and <span class="html-italic">Charoideae</span> and subgenus <span class="html-italic">Caulerpa</span> section <span class="html-italic">Sedoideae</span> and part of section <span class="html-italic">Caulerpa</span> (see <b>b</b>,<b>c</b> for detail of the prune clade). (<b>b</b>): second part: Subgenus <span class="html-italic">Caulerpa</span>, section <span class="html-italic">Caulerpa</span> (see <b>a</b>,<b>c</b> for detail of the prune clade). (<b>c</b>): third part: Subgenus <span class="html-italic">Caulerpa</span>, section <span class="html-italic">Caulerpa</span> (see <b>a</b>,<b>b</b> for detail of the prune clades).</p>
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<p>Illustrations of Caulerpa species found in French Polynesia. (<b>A</b>,<b>B</b>): <span class="html-italic">Caulerpa bikinensis</span>; (<b>C</b>,<b>D</b>): <span class="html-italic">Caulerpa chemnitzia</span>; (<b>E</b>,<b>F</b>): <span class="html-italic">Caulerpa cupressoides</span>; (<b>G</b>,<b>H</b>): <span class="html-italic">Caulerpa nummularia</span>; (<b>I</b>,<b>J</b>): <span class="html-italic">Caulerpa oligophylla</span>; (<b>K</b>,<b>L</b>): <span class="html-italic">Caulerpa pickeringii</span> var. <span class="html-italic">pickeringii</span>; (<b>M</b>,<b>N</b>): <span class="html-italic">Caulerpa pickeringii</span> var. <span class="html-italic">seuratii</span>; (<b>O</b>,<b>P</b>): <span class="html-italic">Caulerpa racemosa</span>; (<b>Q</b>,<b>R</b>): <span class="html-italic">Caulerpa serrulata</span>; (<b>S</b>,<b>T</b>): <span class="html-italic">Caulerpa sertularioides</span>; (<b>U</b>,<b>V</b>): <span class="html-italic">Caulerpa taxifolia</span>; (<b>W</b>,<b>X</b>): <span class="html-italic">Caulerpa urvilleana</span>; (<b>Y</b>,<b>Z</b>): <span class="html-italic">Caulerpa verticillata</span>; (<b>AA</b>,<b>AB</b>): <span class="html-italic">Caulerpa webbiana</span>.</p>
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<p><span class="html-italic">C. pickeringii</span>. (<b>a</b>–<b>h</b>): <span class="html-italic">C. pickeringii</span> var. <span class="html-italic">pickeringii.</span> (<b>a</b>,<b>b</b>): in situ habit; (<b>c</b>,<b>d</b>): herbarium specimens (<b>c</b>: NOU200104; <b>d</b>: NOU200068); (<b>e</b>): cross-section of stolon (NOU200104); (<b>f</b>): close-up on the verticillate ramuli of the stolon (NOU200104); (<b>g</b>): verticillate ramuli around the uprights (NOU200068); (<b>h</b>): dichotomously divided ramuli with dichotomous and mucronate tips (NOU200104); (<b>i</b>–<b>o</b>): <span class="html-italic">C. pickeringii</span> var. <span class="html-italic">seuratii</span>; (<b>i</b>): in situ habit; (<b>j</b>): <span class="html-italic">C. pickeringii</span> var. <span class="html-italic">seuratii</span> ecad <span class="html-italic">major</span> herbarium specimen (NOU200067); (<b>k</b>): <span class="html-italic">C. pickeringii</span> var. <span class="html-italic">seuratii</span> ecad <span class="html-italic">minor</span> herbarium specimen (NOU200126); (<b>l</b>): cross-section of stolon with squama (NOU200126); (<b>m</b>): close-up on the mucronate tips of squama (NOU200126); (<b>n</b>): triseriate ramuli on uprights (NOU200067); (<b>o</b>): undivided branchlets with trichotomous tips (NOU200067). Scale bars: (<b>a</b>): 1.25 cm; (<b>b</b>): 1.10 cm; (<b>c</b>,<b>d</b>): 1 cm; (<b>e</b>,<b>f</b>): 1 mm; (<b>g</b>): 0.3 mm; (<b>h</b>): 0.25 mm; (<b>i</b>): 2.5 cm; (<b>j</b>,<b>k</b>): 1 cm; (<b>l</b>–<b>n</b>): 1 mm; (<b>o</b>): 2 mm.</p>
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18 pages, 4898 KiB  
Article
Abundant Species Govern the Altitude Patterns of Bacterial Community in Natural and Disturbed Subalpine Forest Soils
by Chaonan Li, Haijun Liao, Dehui Li and Yanli Jing
Diversity 2024, 16(4), 242; https://doi.org/10.3390/d16040242 - 18 Apr 2024
Cited by 2 | Viewed by 1079
Abstract
Abundant and rare bacteria exhibit unequal responses to environmental changes and disturbances, potentially resulting in differential contributions to the altitudinal characteristics of total community in natural and disturbed soils. Although the altitude patterns of soil bacteria have been widely studied, it remains unclear [...] Read more.
Abundant and rare bacteria exhibit unequal responses to environmental changes and disturbances, potentially resulting in differential contributions to the altitudinal characteristics of total community in natural and disturbed soils. Although the altitude patterns of soil bacteria have been widely studied, it remains unclear whether these patterns are consistent among bacteria with varying predominance levels, and which subpopulation contributes more to maintaining these patterns in natural and disturbed subalpine forest soils. In this study, we collected 18 natural subalpine forest soil samples and 18 disturbed ones from three altitudes (2900 m a.s.l., 3102 m a.s.l., and 3194 m a.s.l.) along the Wenma highway in Miyaluo, Lixian, Sichuan, Southwest China. By partitioning total bacterial communities based on species predominance, we found that bacteria with higher predominance levels tended to exhibit altitude patterns (α-diversity, community structure, and functional redundancy) similar to those of total bacteria in both natural and disturbed subalpine forest soils, although they only occupied a small portion of the community. Abundant bacteria might play critical roles in maintaining the regional ecological characteristics of total community across the altitude gradient, while the rare and hyper-rare ones might contribute more to local diversity and functional redundancy. In natural soils, the altitude patterns of α-diversity inferred from total, abundant, and rare bacteria were mainly shaped by NO3-N, while soil conductivity mainly drove the altitude patterns of α-diversity inferred from hyper-rare bacteria. Additionally, the community structures of total, abundant, rare, and hyper-rare bacteria were mainly shaped by NO3-N, while the altitude patterns of functional redundancy inferred from total, abundant, and rare bacteria were mainly shaped by soil conductivity in natural soils. In disturbed subalpine forest soils, the influences of NO3-N for the altitude patterns of α-diversity and community structure, and those of soil conductivity for functional redundancy, were relatively weak in total, abundant, rare, and hyper-rare bacteria. This study examined the roles of bacteria with varying predominance levels in maintaining the altitude pattern of bacteria in both natural and disturbed subalpine forest soils, providing novel insights for devising strategies to conserve biodiversity and ecologically restore disturbed soils in subalpine ecosystems. Full article
(This article belongs to the Special Issue Microbiota Diversity in Plants and Forest)
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<p>Shannon–Wiener indices of total, abundant (RB ≥ 0.001%), rare (0.0001% ≤ RB &lt; 0.001%), and hyper-rare (RB &lt; 0.0001%) bacteria in natural (NS) and cut slope (CS) soils (<b>A</b>). The relationships between Shannon–Wiener indices of total soil bacteria and those of abundant, rare, and hyper-rare ones (<b>B</b>). Asterisks in figure (<b>A</b>) represent significant differences between NS and CS at an altitude (* <span class="html-italic">p</span> &lt; 0.05). Lowercase and uppercase letters in figure (<b>A</b>) denote the significance of differences among altitudes within NS and CS, respectively, and it indicates no significant difference (<span class="html-italic">p</span> &lt; 0.05) between two groups if they share the same letter. <span class="html-italic">R</span>-values and <span class="html-italic">p-</span>values in figure (<b>B</b>) represent Pearson correlation coefficients and their associated significance. RB: average relative abundance.</p>
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<p>Bray–Curtis-distance-based non-metric multidimensional scaling (NMDS) analysis for the communities of total (<b>A</b>), abundant (RB ≥ 0.001%) (<b>B</b>), rare (0.0001% ≤ RB &lt; 0.001%) (<b>C</b>), and hyper-rare (RB &lt; 0.0001%) (<b>D</b>) bacteria. NS: natural soils; CS: cut slope soils; RB: average relative abundance.</p>
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<p>Shifts in the relative abundance of differential genera identified by LEfSe analysis for total, abundant (RB ≥ 0.001%), and rare (0.0001% ≤ RB &lt; 0.001%) bacteria (<b>A</b>). The FAPROTAX functions of differential genera (<b>B</b>). Relative abundance values in figure (<b>A</b>) were normalized using <span class="html-italic">log()</span> function in R base package. Numbers within square brackets in figure (<b>A</b>) represent the ASV count associated with each differential genus. Numbers in cells of figure (<b>B</b>) represent the ASV count for each differential genus possessing a particular function (e.g., the <span class="html-italic">Bryobacter</span> possessing 38 ASVs with chemoheterotrophy). Figure (<b>B</b>) only shows differential genera with a known function. NS: natural soils; CS: cut slope soils; RB: average relative abundance; CC: carbon cycling; NC: nitrogen cycling.</p>
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<p>Bray–Curtis-distance-based redundancy analysis (RDA) for the communities of total (<b>A</b>), abundant (RB ≥ 0.001%) (<b>B</b>), rare (0.0001% ≤ RB &lt; 0.001%) (<b>C</b>), and hyper-rare (RB &lt; 0.0001%) (<b>D</b>) bacteria. NS: natural soils; CS: cut slope soils; RB: average relative abundance.</p>
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<p>Functional redundancies of total, abundant (RB ≥ 0.001%), rare (0.0001% ≤ RB &lt; 0.001%), and hyper-rare (RB &lt; 0.0001%) bacteria in natural (NS) and cut slope (CS) soils (<b>A</b>). The relationships between the functional redundancies of total soil bacteria and those of abundant, rare, and hyper-rare ones (<b>B</b>). Asterisks in figure (<b>A</b>) represent the significant differences between NS and CS at an altitude (* <span class="html-italic">p</span> &lt; 0.05, ** <span class="html-italic">p</span> &lt; 0.01). The lowercase and uppercase letters in figure (<b>A</b>) represent the significance of differences among altitudes within NS and CS, respectively, and it indicates no significant difference (<span class="html-italic">p</span> &lt; 0.05) between two groups if they share the same letter. <span class="html-italic">R</span>-values and <span class="html-italic">p-</span>values in figure (<b>B</b>) mean Pearson correlation coefficients and their associated significance. RB: average relative abundance.</p>
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13 pages, 4852 KiB  
Article
Climate-Change-Driven Shifts in Aegilops tauschii Species Distribution: Implications for Food Security and Ecological Conservation
by Shirin Mahmoodi, Mohammad Jaffar Aghaei, Kourosh Ahmadi and Amir Naghibi
Diversity 2024, 16(4), 241; https://doi.org/10.3390/d16040241 - 18 Apr 2024
Cited by 1 | Viewed by 1491
Abstract
Climate change has diverse effects on the planet’s environment, including changes and shifts in the distribution and abundance of species. In this paper, we present a robust prediction ensemble algorithm for the current and future species distribution of Aegilops tauschii. Four modeling [...] Read more.
Climate change has diverse effects on the planet’s environment, including changes and shifts in the distribution and abundance of species. In this paper, we present a robust prediction ensemble algorithm for the current and future species distribution of Aegilops tauschii. Four modeling approaches were trained using various environmental variables (bioclimatic and soil variables) to accurately predict the species distribution for future scenarios. The results showed that GBM and RF demonstrated the most accurate predictions with an Area Under the Receiver Operating Characteristic (ROC) Curve (AUC) of 0.80 and 0.83, respectively. The results of variable importance depicted that the temperature seasonality (bio4) was the most important and effective factor in determining the habitat suitability of Ae. tauschii, followed closely by the precipitation seasonality (bioclimate 15) and the mean temperature of the warmest quarter (bio10). Then, the distribution maps of Ae. tauschii were produced under climate change scenarios for 2050 and 2070. The results showed that Ae. tauschii will lose some of its suitable habitats under climate change and that this loss will be more severe in the east part of the study area. The results of the present study have important implications for ecological conservation as they can assist in identifying critical habitats and inform conservation planning efforts. Our model provides a valuable tool for understanding the potential future distribution of Ae. tauschii and highlights the need for continuous monitoring and protection of this species. Full article
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<p>Map of the study area and distribution of <span class="html-italic">Ae. tauschii</span> in Iran.</p>
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<p>Evaluation of modeling approaches using ROC–TSS curve.</p>
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<p>Variable importance of environmental variables in <span class="html-italic">Ae. tauschii</span> species distribution modeling in Iran. The abbreviations of the environmental variables are as follows: bdod: bulk density of the fine earth fraction, cfvo: a fraction of coarse fragments, N: total nitrogen, gph: pH, bio3: isothermality, bio4: temperature seasonality, bio10: mean temperature of warmest quarter, bio13: precipitation of wettest month, bio15: precipitation seasonality.</p>
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<p>Response curves of <span class="html-italic">Ae. tauschii</span> produced by species distribution models. The abbreviations of the environmental variables are as follows: bdod: bulk density of the fine earth fraction, cfvo: a fraction of coarse fragments, N: total nitrogen, gph: pH, bio3: isothermality, bio4: temperature seasonality, bio10: mean temperature of warmest quarter, bio13: precipitation of wettest month, bio15: precipitation seasonality.</p>
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<p>Current distribution map of <span class="html-italic">Ae. tauschii</span> predicted by ensemble model in the study area.</p>
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<p>Species distribution of <span class="html-italic">Ae. tauschii</span> in the study area under climate change scenarios in 2050 and 2070.</p>
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<p>Range size of <span class="html-italic">Ae. tauschii</span> distribution under different climate change scenarios for 2050 and 2070 in the study area.</p>
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24 pages, 2638 KiB  
Article
Building the Resilience of Marginal Rural Areas Using a Complementary Characterization Approach: Possible Beneficial Health Effects and Stress Tolerance of Italian Common Bean (Phaseolus vulgaris L.) Landraces
by Martina Falcione, Alessandra Renella, Vadym Samukha, Mayra Colardo, Melissa Simiele, Gabriella Stefania Scippa, Marco Segatto and Dalila Trupiano
Diversity 2024, 16(4), 240; https://doi.org/10.3390/d16040240 - 17 Apr 2024
Viewed by 1403
Abstract
Common bean landraces, besides contributing to the preservation of the social and cultural identity of the local communities of the production area, typically display adaptability to adverse agro-climatic conditions. This adapted germplasm is a repository of the gene pool and also shows typical [...] Read more.
Common bean landraces, besides contributing to the preservation of the social and cultural identity of the local communities of the production area, typically display adaptability to adverse agro-climatic conditions. This adapted germplasm is a repository of the gene pool and also shows typical phytochemical profiles, representing an essential source of bioactive components. However, genetic erosion is progressively affecting this genetic material, creating serious threats to its cultivation in marginal rural areas and use as a source of biodiversity and bioproducts. In the present work, a comprehensive approach was used to characterize the seed morpho-colorimetric traits, genetic diversity, and NMR metabolomic profiles of three Italian common bean landraces. Specific physiological and biochemical features (antioxidant molecules, osmolytes, structural reorganization of photosynthetic pigment, etc.), together with the accumulation of distinctive metabolites, contribute to the description of the observed diversity among the landraces in terms of the salt stress response and antiproliferative abilities on intestinal human cancer cells. This information could be useful in establishing their value in terms of environmental and/or human health “service”, both essential to translating landraces into competitive products, a prerequisite for envisioning appropriate strategies for their conservation and a driving force for the revitalization of marginal rural areas. Full article
(This article belongs to the Special Issue Advances in Crop Genetic Diversity: Challenges and Opportunities)
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<p>Analysis of common bean morpho-colorimetric and genetic diversity. Scatter plot of the PCA computed among three populations of common bean (<span class="html-italic">Phaseolus vulgaris</span> L.) using fourteen morpho-colorimetric features (<b>a</b>) and dendrogram resulting from a cluster analysis using the unweighted pair group method with arithmetic mean (UPGMA) with the Euclidean distance index (<b>b</b>). Scatter plot of the PCoA computed on the three bean populations, using eight inter-simple sequence repeat (ISSR) primers (<b>c</b>) and dendrogram resulting from UPGMA clustering (Jaccard similarity index) (<b>d</b>). Phaseolin (Phs) SCAR marker banding patterns. The ladder range is 200–300 base pairs (ApplyChem GmbH, Darmstadt, Germany) (<b>e</b>). CV: Ciliegino; SMR: San Michele Rosso; FDA: Fagiolo d’Acqua.</p>
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<p><sup>1</sup>H NMR metabolomic profile of common bean seed aqueous extracts. <sup>1</sup>H and <sup>13</sup>C chemical shift assignment (δ, ppm) of the 25 metabolites detected in the seed aqueous extract of the common bean population (<b>a</b>). Expanded <sup>1</sup>H NMR spectrum of the San Michele Rosso common bean landrace from: 0.9 to 3.0 ppm (<b>b</b>); 3.0 to 4.5 ppm (<b>c</b>); 4.5 to 5.9 ppm (<b>d</b>); 5.9 to 7.9 ppm (<b>e</b>); 7.9 to 9.2 ppm (<b>f</b>). d: doublet, dd: double doublet; m: multiplet; s: singlet, t: triplet; tp: triple doublet.</p>
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<p>Principal Component Analysis (PCA) and Partial Least Squares Discriminant Analysis (PLS-DA) computed on NMR qualitative data of common bean aqueous seed extracts. Score plot of the PCA (<b>a</b>) and score plot of the PLS-DA (<b>b</b>). CV: Ciliegino; SMR: San Michele Rosso; FDA: Fagiolo d’Acqua.</p>
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<p>Quantification (mg·g<sup>−1</sup>DW) of metabolites in aqueous seed extracts of three common bean landraces. The most intense and distinct metabolite signals of the <sup>1</sup>H NMR spectra have been quantified. Data are expressed as the mean ± standard error and calculated using four replicates. Student’s <span class="html-italic">t</span>-test was performed to determine significant differences (<span class="html-italic">p</span> ≤ 0.05) in the metabolite levels in the common bean populations. Mean values marked with the same letter are not statistically different. CV: Ciliegino; SMR: San Michele Rosso; FDA: Fagiolo d’Acqua.</p>
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<p>Effects of aqueous bean extract administration on cell growth in the Caco-2 cell line. Cell proliferation was assessed in Caco-2 cells treated with vehicle (DMSO, CTR) and CV (<b>a</b>), SMR (<b>b</b>) and FDA (<b>c</b>) aqueous extracts at the doses of 0.1 µg·mL<sup>−1</sup>, 1 µg·mL<sup>−1</sup>, 100 µg·mL<sup>−1</sup>. n = 3 independent experiments. Data represent the means ± standard deviation. Statistical analysis was carried out by using two-way ANOVA, followed by a Bonferroni post hoc test. ** <span class="html-italic">p</span> &lt; 0.01; *** <span class="html-italic">p</span> &lt; 0.001.</p>
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<p>Seed germination under control and salinity stress conditions. Final germination capacity reached by seeds of common bean populations on the last day (8th) of the germination test (<b>a</b>). Germination speed, expressed as T50, of each common bean population under control and salinity stress conditions (<b>b</b>). Germination capacity of Ciliegino (<b>c</b>), San Michele Rosso (<b>d</b>) and Fagiolo d’Acqua (<b>e</b>) under both experimental conditions. Data represent the mean (<span class="html-italic">n</span> = 10) ± standard error. Mean values, marked with the asterisk, are statistically different. Student’s <span class="html-italic">t</span>-test was applied to weigh the effects of different treatments (<span class="html-italic">p</span> ≤ 0.05). Mean values marked with the same letter are not statistically different. CV: Ciliegino; SMR: San Michele Rosso; FDA: Fagiolo d’Acqua.</p>
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<p>Morpho-physiological parameters analyzed in the three common bean landrace populations. Fresh biomass (FW; (<b>a</b>,<b>b</b>)), dry biomass (DW; (<b>d</b>,<b>e</b>)), relative water content (RWC; (<b>g</b>,<b>h</b>)) of roots and leaves and total chlorophyll content (Chl; (<b>c</b>)), chlorophyll A and B ratio (Chl A/Chl B; (<b>f</b>)) and carotenoid content (<b>i</b>) of leaves of the three common populations, grown under controlled and salt stress conditions, were analyzed. Data represent the mean (FW, DW and RWC n = 4; total Chl, Chl A/Chl B, carotenoids n = 3) ± standard error. A Student’s <span class="html-italic">t</span>-test was conducted to weigh the effects of the different growth conditions (<span class="html-italic">p</span> ≤ 0.05). Mean values marked with the same letter are not statistically different. CV: Ciliegino; SMR: San Michele Rosso; FDA: Fagiolo d’Acqua.</p>
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<p>Biochemical parameters analyzed in the three common bean landrace populations. Proline (<b>a</b>,<b>d</b>), total carbohydrates (<b>b</b>,<b>e</b>) and malondialdehyde (MDA; (<b>c</b>,<b>f</b>)) contents were measured in the roots and leaves of the three common populations, grown under controlled and salt stress conditions. Data represent the mean (n = 3) ± standard error. A Student’s <span class="html-italic">t</span>-test was conducted to weigh the effects of the different growth conditions (<span class="html-italic">p</span> ≤ 0.05). Mean values marked with the same letter are not statistically different. CV: Ciliegino; SMR: San Michele Rosso; FDA: Fagiolo d’Acqua.</p>
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15 pages, 1465 KiB  
Article
Terrestrial Tardigrada (Water Bears) of the Słowiński National Park (Northern Poland)
by Tomasz Bartylak, Pushpalata Kayastha, Anastasiia Polishchuk, Milena Roszkowska, Magdalena Maria Bartylak, Tomasz Rutkowski, Michał Zacharyasiewicz and Łukasz Kaczmarek
Diversity 2024, 16(4), 239; https://doi.org/10.3390/d16040239 - 17 Apr 2024
Viewed by 1087
Abstract
In this paper, samples of mosses, lichens and cryptogams (mosses mixed with lichens) collected from Słowiński National Park (northern Poland) were studied for water bears (Tardigrada). In total, 27 tardigrade taxa were identified: 21 to the species level, one identified as „cf. [...] Read more.
In this paper, samples of mosses, lichens and cryptogams (mosses mixed with lichens) collected from Słowiński National Park (northern Poland) were studied for water bears (Tardigrada). In total, 27 tardigrade taxa were identified: 21 to the species level, one identified as „cf.” and three to the genus level, with six species (Eremobiotus ginevrae, Hypsibius dujardini, Hypsibius scabropygus, Milnesium beasleyi, Minibiotus intermedius and Notahypsibius pallidoides) being new records for Poland. Two possibly new for science species were also found, belonging to genera Diphascon and Mesobiotus. Additionally, a very rare eutardigrade Pseudohexapodibius degenerans has been found in the samples analyzed in the present study for the first time outside of the type locality. The effects of habitat and substrate on species richness were also investigated and showed no significant differences between mosses and lichens, as well as all substrates except for concrete walls. Full article
(This article belongs to the Special Issue 2024 Feature Papers by Diversity’s Editorial Board Members)
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<p>Map of sampling sites. Dashed line indicates area of the SPN. Striped field indicates area covered by sand dunes. Red dots indicate sampling sites.</p>
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<p>Rarefaction and extrapolation for habitats. (<b>A</b>) Sample-size-based rarefaction and extrapolation sampling curve; (<b>B</b>) sample completeness curve; (<b>C</b>) coverage-based rarefaction and extrapolation sampling curve. The solid lines of the curves represent rarefaction, the dashed lines represent extrapolation and the shaded areas represent the 95% confidence intervals (based on a bootstrap method with 100 replications).</p>
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<p>Rarefaction and extrapolation for substrates. (<b>A</b>) Sample-size-based rarefaction and extrapolation sampling curve; (<b>B</b>) sample completeness curve; (<b>C</b>) coverage-based rarefaction and extrapolation sampling curve. The solid lines of the curves represent rarefaction, the dashed lines represent extrapolation and the shaded areas represent the 95% confidence intervals (based on a bootstrap method with 100 replications).</p>
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<p>Venn diagrams of species richness (<b>A</b>) for habitats and (<b>B</b>) for substrates.</p>
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13 pages, 3169 KiB  
Article
Outstanding Aggregation of the Atlantic Brisingid Hymenodiscus coronata (Sars, 1871) (Echinodermata: Asteroidea) in the Strait of Sicily
by Margherita Toma, Antonio Giova, Marzia Bo, Simonepietro Canese, Francesco Enrichetti, Teresa Romeo, Eva Salvati and Silvestro Greco
Diversity 2024, 16(4), 238; https://doi.org/10.3390/d16040238 - 17 Apr 2024
Viewed by 1065
Abstract
The sea star Hymenodiscus coronata is the only Mediterranean representative of the deep-sea order Brisingida. In the North-eastern Atlantic Ocean, this species is known to create dense aggregations, while, in the Mediterranean basin, it is generally reported as scattered individuals. Through the analysis [...] Read more.
The sea star Hymenodiscus coronata is the only Mediterranean representative of the deep-sea order Brisingida. In the North-eastern Atlantic Ocean, this species is known to create dense aggregations, while, in the Mediterranean basin, it is generally reported as scattered individuals. Through the analysis of the video footage obtained from an extensive ROV campaign carried out in the northern Strait of Sicily in 2021, over 2850 specimens were counted. The specimens, observed between 310 m and 714 m depth, showed a large variability in size and number of arms. It was noted that 17% of the specimens displayed the peculiar “sail position”, with all the arms extended vertically in the water column, possibly increasing the filtration rate. Almost the totality of the individuals was noted on soft bottoms, in accordance with the ecological preferences of the species. The density of H. coronata in each site varied between 0.01 and 0.81 individuals m−2, with the highest densities reported in sites characterized by large muddy areas among rocky outcrops and turbulent hydrodynamic conditions. Although the trawling areas exploited in 2021 did not seem to interfere with the presence of H. coronata in the study area, a precautionary approach should be assumed to protect the largest ever reported Mediterranean aggregation of this poorly known species. Full article
(This article belongs to the Special Issue Diversity and Biogeography of Sea Stars (Echinodermata, Asteroidea))
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<p>Study area. Multi-beam bathymetric model (5 m resolution) of the explored area (Strait of Sicily, Central Mediterranean Sea, inset, red rectangle), with the 140 ROV transects (white lines).</p>
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<p>Bathymetric distribution. Boxplot of the bathymetric distribution of <span class="html-italic">Hymenodiscus coronata</span> in the present work (left, orange) and of the 140 ROV transects performed (right, blue).</p>
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<p>Morphology. Frequency (%) of the target sea star <span class="html-italic">H. coronata</span> in terms of (<b>A</b>) size (Small, &lt;15 cm; Medium, 16–30 cm; and Large, &gt;30 cm), (<b>B</b>) number of intact arms, and (<b>C</b>) position on the seafloor.</p>
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<p>Morphology and ecology. ROV images of the sea star <span class="html-italic">H. coronata</span>: (<b>A</b>) close-up of a large specimen on mud, with well-visible spines on the eight slender arms and the gonads at the base of the arms; (<b>B</b>) two different-sized individuals with the arms slightly lifted; (<b>C</b>) several large specimens of <span class="html-italic">H. coronata</span> showing arms of different sizes flatted on the muddy bottom (white arrows); (<b>D</b>) close individuals of different size and number of arms (white arrows); (<b>E</b>) large specimen on the horizontal muddy substrate with the arms’ tips lifted; and (<b>F</b>) <span class="html-italic">H. coronata</span> in the “sail position”. (<b>G</b>,<b>H</b>) <span class="html-italic">Chlorophthalmus agassizi</span> and <span class="html-italic">Benthocometes robustus</span> are among the bentho-nektonic species frequently observed close to the target sea stars. Scale bar: 15 cm.</p>
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<p>Population density and fishing impact. Distribution of the transects in which <span class="html-italic">H. coronata</span> was observed, with the indication of the maximum density per sampling unit and the trawling areas exploited in 2021.</p>
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<p>Population density and ecological preferences. Distribution of the specimens (red dots) along the transects (white lines) according to substrate type and inclination: (<b>A</b>–<b>D</b>) horizontal or slightly inclined muddy substrates with sparse rocks; and (<b>E</b>–<b>H</b>) sloping to vertical rocky outcrops with scattered muddy patches. Scale bar: 250 m.</p>
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<p>Patchiness. Maximum density per sampling unit related to the substrate type (grey, outcropping rocks; and light yellow, mud) in four selected transects: (<b>A</b>) Dive 60; (<b>B</b>) Dive 88; (<b>C</b>) Dive 94; and (<b>D</b>) Dive 83.</p>
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17 pages, 2210 KiB  
Article
Molecular and Morphological Phylogenies of Spirorbinae (Serpulidae, Polychaeta, Annelida) and the Evolution of Brooding Modes
by Greg W. Rouse, Tara A. Macdonald and Elena K. Kupriyanova
Diversity 2024, 16(4), 237; https://doi.org/10.3390/d16040237 - 17 Apr 2024
Viewed by 1440
Abstract
Spirorbinae, a ubiquitous group of marine calcareous tubeworms with a small body size as adults, have a fascinating diversity of brooding modes that form the basis for their taxonomic division into six tribes (traditionally subfamilies): in-tube incubation, with varying degrees of attachment to [...] Read more.
Spirorbinae, a ubiquitous group of marine calcareous tubeworms with a small body size as adults, have a fascinating diversity of brooding modes that form the basis for their taxonomic division into six tribes (traditionally subfamilies): in-tube incubation, with varying degrees of attachment to adult structures (four tribes), and external incubation in a modified radiole (opercular brood chambers; two tribes). We investigated the evolutionary transitions among these brooding modes. Phylogenetic reconstruction with molecular (28s and 18s rDNA) and morphological data (83 characters) among 36 taxa (32 ingroup spirorbins; 4 filogranin outgroups) of the combined data set, using maximum parsimony, maximum likelihood, and Bayesian analyses, inferred Spirorbinae to be monophyletic, with strong support for the monophyly for five tribes (Circeini, Januini, Romanchellini, Paralaeospirini and Spirorbini), but non-monophyly for Pileolariini. However, deeper relationships among some tribes remain unresolved. Neomicrorbis was found to be the sistergroup to all other Spirorbinae. Alternative coding strategies for assessing the ancestral state reconstruction for the reproductive mode allowed for a range of conclusions as to the evolution of tube and opercular brooding in Spirorbinae. Two of the transformations suggest that opercular brooding may be ancestral for Spirorbinae, and the tube-incubating tribes may have been derived independently from opercular-brooding ancestors. Full article
(This article belongs to the Special Issue Diversity in 2023)
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<p>Representatives of Spirorbinae. (<b>A</b>) <span class="html-italic">Neomicrorbis</span> cf. <span class="html-italic">azoricus</span>: preserved specimen removed from the tube with a whole tube at a smaller scale. (<b>B</b>) <span class="html-italic">Amplicaria spiculosa</span>: live specimen with a distinctive hooked operculum and brood in the operculum (arrow). (<b>C</b>) Live <span class="html-italic">A. spiculosa</span> anterior showing brood chamber (arrow). (<b>D</b>) <span class="html-italic">Janua heterostropha</span> in the tube; arrow indicates opercular brood chamber, used for only one brood. (<b>E</b>) Closeup of operculum of <span class="html-italic">J. heterostropha</span> showing well-developed larvae. (<b>F</b>) Larva of <span class="html-italic">J. heterostropha</span> showing paired larval attachment glands. (<b>G</b>) An opened tube of <span class="html-italic">Circeis spirillum</span>, showing embryos adhering to each other and the tube wall (arrow). (<b>H</b>) <span class="html-italic">Spirorbis</span> cf. <span class="html-italic">tridentatus</span> removed from the tube, showing an embryo string that is attached to the posterior inner surface of the tube. (<b>I</b>) <span class="html-italic">Pileolaria</span> sp. (Pileolariini) (from Bondi, Australia and not included in this study) with an epithelial opercular brood chamber, used for more than one brood (arrow). (<b>J</b>) <span class="html-italic">Metalaeospira tenuis</span> with an unattached brood string (arrow). (<b>K</b>) <span class="html-italic">Helicosiphon biscoeensis</span> removed from the tube and in the tube at a smaller scale. (<b>L</b>) <span class="html-italic">Paralaeospira</span> sp. from Tasmania (and not included in this study) removed from the tube with its loose embryo string (arrow). (<b>M</b>) <span class="html-italic">Protolaeospira</span> sp.: arrow indicates thoracic brood stalk, attaching brood mass to the adult body.</p>
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<p>Strict consensus tree of 28 most parsimonious trees (297 steps) derived from the 83-character morphology matrix using PAUP*.</p>
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<p>Maximum likelihood tree with branch lengths derived from the morphology plus molecular (18S rDNA, 28S rDNA) concatenated datasets. The MP and Bayesian analyses gave the same tree topology. Numbers at nodes are ML and MP bootstrap (BS) values followed by Bayesian posterior probability (PP). BS values below 50 and posterior probabilities below 0.7 are not shown. A * indicates that both BS scores were 95 or greater, and the PP was 1.</p>
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<p>Transformation for three versions of characters based on brooding mode mapped onto the ML tree topology, visualized in Mesquite 3.81 using likelihood ancestral state reconstruction on ball and sticks tree form, with the Mk1 probability model. (<b>A</b>) Brooding general character with four states, only two of which occur in Spirorbinae, in the tube or in the operculum. (<b>B</b>) Opercular brooding only character with three states, two for kinds of opercular brooding. (<b>C</b>) Brooding character with eight states to cover the various forms of tube brooding and with only one state for opercular brooding. Numerical values at the nodes show the maximum likelihood score, as a proportion of 1, for the most likely state. The ancestral state for Spirorbinae for Brooding (<b>C</b>) is unknown owing to the lack of knowledge for <span class="html-italic">Neomicrorbis</span> cf. <span class="html-italic">azoricus</span>.</p>
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20 pages, 4129 KiB  
Review
Anthropogenic Pressures on Gorillas: A Case of Grauer’s Gorillas in Maiko National Park, the Democratic Republic of Congo
by Kahindo Tulizo Consolee, Xiaofeng Luan and Li Cong
Diversity 2024, 16(4), 236; https://doi.org/10.3390/d16040236 - 16 Apr 2024
Viewed by 1550
Abstract
Anthropogenic activities put biodiversity under pressure, adversely affecting the forest ecosystem and wildlife habitats. Habitat disturbance and modification are among the main threats to animal populations in tropical forests. In the Democratic Republic of Congo (DRC), Grauer’s gorillas (Gorilla beringei graueri) [...] Read more.
Anthropogenic activities put biodiversity under pressure, adversely affecting the forest ecosystem and wildlife habitats. Habitat disturbance and modification are among the main threats to animal populations in tropical forests. In the Democratic Republic of Congo (DRC), Grauer’s gorillas (Gorilla beringei graueri) are continuously threatened through forest encroachment for agricultural expansion, human settlements, new refugee camps, illegal logging, and mining across the country. Moreover, poaching and bushmeat trafficking continuously threaten gorillas’ existence. These drivers increase the proximity of humans and the risk of disease transmission. The emerging and existing zoonotic diseases, including Ebola, are continuously impacting gorillas’ lives. All of these pressures combined are disrupting natural behavior patterns and are leading to the decline in the Grauer’s gorillas’ population. Therefore, this review scrutinizes findings on the anthropogenic pressures on the habitats and survival of Grauer’s gorillas. Also, it is important to engage with people for the shared conservation role and ecotourism to support the conservation of forest biodiversity and Grauer’s gorillas’ habitats, particularly for the Maiko National Park in the DRC. Full article
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<p>Maiko National Park map.</p>
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<p>Schematic representation of the effects of anthropogenic activities on natural resources, forests, and gorillas habitats in the Democratic Republic of Congo.</p>
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<p>Anthropogenic pressure to gorillas and gorillas’ habitat. (<b>A</b>) Illegal mining site in the park. (<b>B</b>) Forest encroachment and deforestation. (<b>C</b>) Spent remains of gun bullet cartridges.</p>
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<p>The role of bridging organizations and traditional knowledge in co-management of natural resources and forest conservation.</p>
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14 pages, 5363 KiB  
Article
Effects of Land Use Change on Avian Diversity in the Semi-Arid Area of Longxi Loess Plateau
by Ruirui Mao, Dexi Zhang, Qian Zhou, Yizhu Wang and Lixun Zhang
Diversity 2024, 16(4), 235; https://doi.org/10.3390/d16040235 - 16 Apr 2024
Viewed by 1255
Abstract
Biodiversity is under threat due to human-induced changes in land use. While various aspects of biodiversity are increasingly studied in response to these changes, there is limited understanding of their effects on the structure and composition of bird communities in dryland regions. We [...] Read more.
Biodiversity is under threat due to human-induced changes in land use. While various aspects of biodiversity are increasingly studied in response to these changes, there is limited understanding of their effects on the structure and composition of bird communities in dryland regions. We examined the impacts of land use change on birds in the semi-arid area of the Longxi Loess Plateau by considering taxonomic diversity, functional diversity, and phylogenetic diversity. We analyzed both the α- and β-diversity of avian communities across different dimensions of diversity and calculated functional and phylogenetic structures using the net relatedness index. Our findings revealed that species richness was highest in farmland and abandoned farmland, while artificial mixed forests exhibited the highest number of unique species. Functional and phylogenetic α-diversity was greater in farmland and abandoned farmland when compared to the other four land use types. Moreover, the taxonomic diversity in artificial mixed forests, artificial Caragana korshinskii forests, and artificial Platycladus orientalis forests surpassed that in typical grasslands, but no differences were observed in functional and phylogenetic diversity. Regarding β-diversity, turnover patterns dominated multidimensional dissimilarity, with taxonomic turnover and total dissimilarity lower than their functional counterparts but higher than phylogenetic counterparts. Based on the present findings, we emphasize the long-term cessation of ongoing silvicultural initiatives to safeguard bird diversity in the semi-arid region of the Longxi Loess Plateau. This is crucial for narrowly distributed species such as Alectoris magna, as they face heightened vulnerability to losses. Full article
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<p>Sampling sites of birds in different land use types.</p>
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<p>UpSetR intersection diagram displaying the unique and shared bird species among the different land use types. Land use type codes were as follows: PFL—planting farmland; AFL—abandoned farmland; TGL—typical grassland; AMF—artificial mixed forest; ACK—artificial <span class="html-italic">Caragana korshinskii</span> forest; APO—artificial <span class="html-italic">Platycladus orientalis</span> forest.</p>
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<p>Pairwise comparisons of bird community similarity showing the original shared species numbers below the diagonal. The ANOSIM sample R and significance marker are shown above the diagonal separation, where the depth of gray indicates a larger R-value. Land use type codes were as follows: PFL—planting farmland; AFL—abandoned farmland; TGL—typical grassland; AMF—artificial mixed forest; ACK—artificial <span class="html-italic">Caragana korshinskii</span> forest; APO—artificial <span class="html-italic">Platycladus orientalis</span> forest. Asterisks indicate statistically significant in different land use types: “*” 0.05, “**” 0.01.</p>
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<p>The taxonomic diversity (<b>a</b>), functional diversity (<b>b</b>), and phylogenetic diversity (<b>c</b>) of bird communities in six different land use types. Land use type codes are as follows: PFL—planting farmland; AFL—abandoned farmland; TGL—typical grassland; AMF—artificial mixed forest; ACK—artificial <span class="html-italic">Caragana korshinskii</span> forest; APO—artificial <span class="html-italic">Platycladus orientalis</span> forest.</p>
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<p>(<b>a</b>,<b>b</b>) represent multiple comparisons of the functional and phylogenetic structure of bird communities were conducted across various land use types. FD—functional diversity; PD—phylogenetic diversity; NRI—net relatedness index. Land use type codes are as follows: PFL—planting farmland; AFL—abandoned farmland; TGL–typical grassland; AMF—artificial mixed forest; ACK—artificial <span class="html-italic">Caragana korshinskii</span> forest; APO—artificial <span class="html-italic">Platycladus orientalis</span> forest.</p>
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<p>Comparison among different components of taxonomic (<b>a</b>), functional (<b>b</b>) and phylogenetic β-diversity (<b>c</b>) in birds. TD—taxonomic diversity; FD—functional diversity; PD—phylogenetic diversity; sor—Sørensen dissimilarity; sim—turnover; sne—nestedness.</p>
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25 pages, 11154 KiB  
Article
The Diversity of Subterranean Terrestrial Arthropods in Resava Cave (Eastern Serbia)
by Nikola Vesović, Christo Deltshev, Plamen Mitov, Dragan Antić, Dalibor Z. Stojanović, Dejan V. Stojanović, Katarina Stojanović, Milenka Božanić, Aleksandra Ignjatović-Ćupina and Srećko Ćurčić
Diversity 2024, 16(4), 234; https://doi.org/10.3390/d16040234 - 16 Apr 2024
Viewed by 3574
Abstract
The Balkan region is rich in limestone deposits, which have created one of the largest hotspots of subterranean biodiversity. This paper gives an overview of the diversity of subterranean terrestrial arthropods in Resava Cave in eastern Serbia. This cave is protected and has [...] Read more.
The Balkan region is rich in limestone deposits, which have created one of the largest hotspots of subterranean biodiversity. This paper gives an overview of the diversity of subterranean terrestrial arthropods in Resava Cave in eastern Serbia. This cave is protected and has the status of a natural monument. At the same time, it is one of the most visited caves in Serbia and its surroundings. Our study comprises the results of three years of biospeleological investigations of the famous Serbian cave in combination with data from the few available literature sources on the arthropod fauna of the cave. The arthropod samples were collected both manually and with pitfall traps. A total of 107 arthropod species from the four major subphyla were registered in the cave: 66 species of Hexapoda, 27 species of Chelicerata, 11 species of Myriapoda and three species of Crustacea. For four troglobitic, 16 troglophilic and 87 trogloxenic species recorded in the cave, descriptions of their microhabitats and information on their distribution in the cave are given. Considering the medium size of Resava Cave and the lack of permanent water flow in the two main levels on the one hand, and the large number of arthropod species recorded on the other, the cave is relatively rich in hypogean terrestrial arthropod fauna compared to other caves in Serbia that have been biospeleologically studied so far. Full article
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<p>A map of Serbia with karst areas and the location of Resava Cave (red pin) (modified after [<a href="#B18-diversity-16-00234" class="html-bibr">18</a>]). The carbonate platforms of the Carpatho-Balkanides in eastern and southeastern Serbia are framed by the dotted lines. AL—Albania; BA—Bosnia and Herzegovina; BG—Bulgaria; HR—Croatia; HU—Hungary; KTCP—Kučaj-Tupižnica carbonate platform; MCP—Miroč carbonate platform; ME—Montenegro; MK—North Macedonia; RO—Romania.</p>
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<p>Karst landscapes of the Carpatho-Balkanides in eastern Serbia. (<b>A</b>) Lazar’s Canyon, Kučajske Planine Mts.; (<b>B</b>) Suva Prerast, Vratna Gates, Mt. Miroč; (<b>C</b>) one of the peaks of Mt. Stol; (<b>D</b>) the ridge of Mt. Veliki Krš. Photos: N. Vesović.</p>
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<p>Resava Cave in eastern Serbia. (<b>A</b>) The cave entrance seen from the inside; (<b>B</b>) flowstone formation in the Menza Gallery; (<b>C</b>) formation of a new stalactite in the presence of trickling water; (<b>D</b>) corallite speleothems, a feature of the Coral Canals; (<b>E</b>) manual collection of hypogean terrestrial arthropods. Photos: N. Vesović and S. Ćurčić.</p>
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<p>A plan of Resava Cave showing the sites where the arthropod fauna was sampled with pitfall traps (red squares) (modified after [<a href="#B15-diversity-16-00234" class="html-bibr">15</a>]). 1—entrance; 2—Entrance Hall; 3—Hall of Conjoined Columns; 4—Beehive Hall; 5—Canyon (=Dry) Canal; 6—Vestibule of History; 7—Crystal Hall; 8—Concert Hall (=Hall of Statues); 9—Boban’s Hall; 10—Menza Gallery; 11—Coral Canals; 12—Kepa’s (=Mud) Hall. Halls 6 and 7 are connected by an artificial tunnel.</p>
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<p>Troglobitic arthropods from Resava Cave. (<b>A</b>) A male of the spider <span class="html-italic">Centromerus serbicus</span>; (<b>B</b>) a female of <span class="html-italic">C</span>. <span class="html-italic">serbicus</span>; (<b>C</b>) the millipede <span class="html-italic">Serbosoma kucajense</span>; (<b>D</b>) the dipluran <span class="html-italic">Plusiocampa christiani</span>; (<b>E</b>) the ground beetle <span class="html-italic">Duvalius petrovici</span>. Photos: N. Vesović.</p>
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<p>Selected troglophilic arthropods of Resava Cave. (<b>A</b>) The harvestmen <span class="html-italic">Paranemastoma sillii</span>; (<b>B</b>) the spider <span class="html-italic">Meta menardi</span>; (<b>C</b>) the spider <span class="html-italic">Metellina merianae</span>; (<b>D</b>) the tick <span class="html-italic">Ixodes vespertilionis</span>; (<b>E</b>) the isopod <span class="html-italic">Hyloniscus</span> cf. <span class="html-italic">riparius</span>; (<b>F</b>) the millipede <span class="html-italic">Trachysphaera</span> sp.; (<b>G</b>) the springtail <span class="html-italic">Tomocerus vulgaris</span>; (<b>H</b>) the springtail <span class="html-italic">Pygmarrhopalites pygmaeus</span>; (<b>I</b>) the cricket <span class="html-italic">Troglophilus neglectus</span>; (<b>J</b>) the ground beetle <span class="html-italic">Laemostenus punctatus</span>; (<b>K</b>) the rove beetle <span class="html-italic">Quedius mesomelinus</span>; (<b>L</b>) the dipteran <span class="html-italic">Speolepta leptogaster</span>. Photos: N. Vesović.</p>
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<p>Selected trogloxenic arthropods from Resava Cave. (<b>A</b>) The pseudoscorpion <span class="html-italic">Neobisium carpaticum</span>; (<b>B</b>) the harvestmen <span class="html-italic">Lacinius dentiger</span>; (<b>C</b>) the harvestmen <span class="html-italic">Opilio ruzickai</span>; (<b>D</b>) the spider <span class="html-italic">Liocranum rupicola</span>; (<b>E</b>) the spider <span class="html-italic">Philodromus margaritatus</span>; (<b>F</b>) the centipede <span class="html-italic">Lithobius forficatus</span>; (<b>G</b>) the millipede <span class="html-italic">Megaphyllum bosniense</span>; (<b>H</b>) the millipede <span class="html-italic">Polydesmus subscabratus</span>; (<b>I</b>) the psocodean <span class="html-italic">Bertkauia lucifuga</span>; (<b>J</b>) the ground beetle <span class="html-italic">Molops piceus</span>; (<b>K</b>) the herald moth—<span class="html-italic">Scoliopteryx libatrix</span>; (<b>L</b>) the yellow shell moth—<span class="html-italic">Camptogramma bilineata</span>; (<b>M</b>) the caddisfly <span class="html-italic">Stenophylax permistus</span>; (<b>N</b>) the ichneumonid wasp <span class="html-italic">Lymantrichneumon disparis</span>; (<b>O</b>) the dipteran <span class="html-italic">Heleomyza serrata</span>. Photos: N. Vesović.</p>
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22 pages, 10066 KiB  
Article
Resilience of Aboveground Biomass of Secondary Forests Following the Abandonment of Gold Mining Activity in the Southeastern Peruvian Amazon
by Jorge Garate-Quispe, Marx Herrera-Machaca, Victor Pareja Auquipata, Gabriel Alarcón Aguirre, Sufer Baez Quispe and Edgar Eloy Carpio-Vargas
Diversity 2024, 16(4), 233; https://doi.org/10.3390/d16040233 - 15 Apr 2024
Viewed by 1566
Abstract
Amazon rainforests are critical for providing a wide range of ecosystem services. In the Southeastern Peruvian Amazon; however, goldmining activities are causing severe soil degradation and forest loss. We analyzed aboveground biomass (AGB), forest structure, and species diversity recovery during secondary succession in [...] Read more.
Amazon rainforests are critical for providing a wide range of ecosystem services. In the Southeastern Peruvian Amazon; however, goldmining activities are causing severe soil degradation and forest loss. We analyzed aboveground biomass (AGB), forest structure, and species diversity recovery during secondary succession in 179 forest plots. Our study provides the first field-based quantification of AGB recovery following the abandonment by two types of goldmining (heavy machinery and suction pumping) in Madre de Dios (Peru). We found that successional secondary forests in areas subjected to suction pumping were more resilient than those in areas subjected to heavy machinery. After 20 years, mean AGB in suction pumping mining areas had reached 56% of reference forest AGB, while in areas of heavy machinery mining it was only 18%. Mining type, stand age, and distance from the forest edge had a significant effect on AGB. The influence of the distance from the forest edge on AGB varies according to mining type because the effects of species diversity on AGB are mediated by the distance from the forest edge. Our results clearly showed the dynamics of AGB recovery across a secondary succession after goldmining, and the contrasting responses of AGB between the two mining types. Our study disentangles the importance of key factors in forest recovery after mining and improves understanding of the resilience of biomass accumulation in these highly degraded ecosystems. Full article
(This article belongs to the Special Issue Plant Succession and Vegetation Dynamics)
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<p>Map of the study area in Peru (<b>a</b>) and in Madre de Dios (<b>b</b>), Southeastern Peruvian Amazon. (<b>c</b>) Landsat-8 images (July 2023) over the study. It shows the location of field sites in the study, and representative photos of the type of mining.</p>
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<p>Results of structural equation models (SEM) showing the relationship between aboveground biomass (AGB), stand age (Age), distance from the forest edge (Distance), and number of species (Species) according to type of mining (heavy machinery and suction pumping). The blue arrows indicate positive effects, while the red arrows indicate negative effects. The dash and plain line types represent the non-significant (<span class="html-italic">p</span> &gt; 0.05) and significant (<span class="html-italic">p</span> &lt; 0.05) paths, respectively. For each path, a standardized regression coefficient value is shown. * Indicates the significant paths at 0.001. (<b>A</b>) = global SEM results, without differentiating by type of mining activities (heavy machinery and suction pumping); (<b>B</b>) = heavy machinery; and (<b>C</b>) = suction pumping.</p>
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<p>Comparison of AGB, species diversity and forest structure among forest plots in two types of mining activities (heavy machinery and suction pumping) according to five recovery age classes of natural regeneration and in reference forest of tree community across a chronosequence in degraded lands of the Peruvian Amazon. (<b>A</b>,<b>B</b>) AGB, (<b>C</b>,<b>D</b>) mean height, (<b>E</b>,<b>F</b>) mean DBH, and (<b>G</b>,<b>H</b>) species diversity (Hill <sup>0</sup>D). Different letters indicate significant differences among age classes for each variable (<span class="html-italic">p</span> &lt; 0.05).</p>
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<p>Relationship between aboveground biomass and stand age of tree community in two types of mining activities (heavy machinery and suction pumping) across a chronosequence in degraded lands of the Peruvian Amazon (<b>A</b>). Mean AGB (±standard error) of reference forests close to plots in degraded lands (<b>B</b>). SEE = standard error of estimate. The blue and red shading around each regression line represent the 95% confidence interval. The solid red circles represent data from a heavy machinery mining. The solid blue circles represent data from a suction pumping mining.</p>
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<p>Non-metric multidimensional scaling ordinations (nMDS) of tree community composition (beta diversity) based on Chao–Jaccard similarity between natural regeneration across a chronosequence in degraded lands of the Peruvian Amazon. (<b>A</b>) Study sites, (<b>B</b>) type of mining, (<b>C</b>) stand age. In B and C, hulls overlaid for each variable. In each nMDS, different letters of the legend label indicate statistically significant differences according to pairwise PERMANOVA tests.</p>
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18 pages, 2387 KiB  
Article
The Occurrence of the American Burying Beetle (Nicrophorus americanus) and Associated Silphid Beetle Community in South Dakota: Implications for Managed Relocation
by William Wyatt Hoback, Daniel G. Snethen, Melissa Reed and Michael C. Cavallaro
Diversity 2024, 16(4), 232; https://doi.org/10.3390/d16040232 - 13 Apr 2024
Viewed by 1184
Abstract
The American burying beetle, Nicrophorus americanus Olivier (Coleoptera: Siliphidae), is a federally threatened species in the United States, occurring in less than 10% of its historic range. The continued monitoring of extant populations found in South Dakota, the northernmost edge of its confirmed [...] Read more.
The American burying beetle, Nicrophorus americanus Olivier (Coleoptera: Siliphidae), is a federally threatened species in the United States, occurring in less than 10% of its historic range. The continued monitoring of extant populations found in South Dakota, the northernmost edge of its confirmed range, is imperative to future conservation efforts, especially with the predicted loss of the species in southern regions because of climate change. Proposed strategies to preserve the species include the reintroduction or translocation of individuals from habitats that have become unsuitable. Beyond adequate habitat and carrion resource requirements, community-level silphid interactions may challenge these efforts because of competition. From 2018 to 2020, we used 80 carrion-baited pitfall traps per year to conduct two 5-day surveys in June and August. A total of 25,923 Silphidae belonging to 15 species were collected in 1200 trap nights. Cumulatively, 1150 N. americanus were captured and marked with 263 recaptures. Like past findings, N. americanus was concentrated in western Tripp County with limited occurrence in Gregory and Todd Counties, suggesting no expansion of their known range in the past decade. Generalized linear mixed-effects models indicated N. americanus abundance was significantly predicted by the co-occurrence of the carrion beetles Oieceoptoma inaequale F. and Oiceoptoma noveboracense Forster, whereas pitfall trap catches dominated by the burying beetle Nicrophorus marginatus F. had predictively less N. americanus. Collectively, these data provide insights into the existing, northernmost N. americanus population dynamics and silphid beetle communities. Concurrent with monitoring extant populations, the characterization of silphid communities that co-occur with N. americanus may provide much-needed information for managed relocation opportunities. Full article
(This article belongs to the Special Issue Genetic Diversity, Ecology and Conservation of Endangered Species)
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<p>Counties sampled from 2018 to 2020 to determine presence of American burying beetles (ABB).</p>
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<p>Hot spot analysis for the occurrence of American burying beetle in Tripp County, South Dakota, from 2018 to 2020. Red indicates traps with more likely occurrence (hot spots), and blue indicates traps with more likely absence of <span class="html-italic">N. americanus</span> (cold spots) among 155 trap locations.</p>
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<p>Hot spot analysis for occurrence of American burying beetle (ABB) in Tripp County, South Dakota, using only 2020 trap locations among 52 trap locations sampled in June and August. Red indicates traps with more likely occurrence (hot spots), and blue indicates traps with more likely absence of ABB (cold spots).</p>
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<p>Spearman’s rank correlation heat map for cumulative silphid beetle captures from 2018 to 2020 in South Dakota. (Species abbreviations: ABB, <span class="html-italic">Nicrophorus americanus</span>; Carol, <span class="html-italic">Nicrophorus carolinus</span>; Gutt, <span class="html-italic">Nicrophorus guttula</span>; Marg, <span class="html-italic">Nicrophorus marginatus</span>; Obscur, <span class="html-italic">Nicrophorus obscurus</span>; Orbic, <span class="html-italic">Nicriophorus orbicollis</span>; Pust, <span class="html-italic">Nicrophorus pustulatus</span>; Tomen, <span class="html-italic">Nicrophorus tomentosus</span>; Necro, <span class="html-italic">Necrophila americana</span>; Surin, <span class="html-italic">Necrodes surinamensis</span>; Ramo, <span class="html-italic">Heterosilpha ramose</span>; Inaequ, <span class="html-italic">Oiceoptoma inaequale</span>; Nova, <span class="html-italic">Oiceoptoma noveboracense</span>; Lappo, <span class="html-italic">Thanatophilus lapponicus</span>; Trunc, <span class="html-italic">Thanatophilus truncates</span>).</p>
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<p>Non-metric multidimensional scaling (nMDS) plot of silphid species collected from 2018 to 2020, where trap sites are categorized by <span class="html-italic">N. americanus</span> abundance (Stress = 0.13). Species abbreviations are as follows: ABB, <span class="html-italic">Nicrophorus americanus</span>; Carol, <span class="html-italic">Nicrophorus carolinus</span>; Gutt, <span class="html-italic">Nicrophorus guttula</span>; Marg, <span class="html-italic">Nicrophorus marginatus</span>; Obscur, <span class="html-italic">Nicrophorus obscurus</span>; Orbic, <span class="html-italic">Nicriophorus orbicollis</span>; Pust, <span class="html-italic">Nicrophorus pustulatus</span>; Tomen, <span class="html-italic">Nicrophorus tomentosus</span>; Necro, <span class="html-italic">Necrophila americana</span>; Surin, <span class="html-italic">Necrodes surinamensis</span>; Ramo, <span class="html-italic">Heterosilpha ramosa</span>; Inaequ, <span class="html-italic">Oiceoptoma inaequale</span>; Nove, <span class="html-italic">Oiceoptoma noveboracense</span>; Lappo, <span class="html-italic">Thanatophilus lapponicus</span>; Trunc, <span class="html-italic">Thanatophilus truncatus</span>.</p>
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16 pages, 5185 KiB  
Article
The Effects of Infectious Diseases on the Consequences of Interspecific Competition in Grassland Communities
by Yanli Chen, Yanping Liu, Xiaoni Liu, Zhengzhong Zhang and Feng Zhang
Diversity 2024, 16(4), 231; https://doi.org/10.3390/d16040231 - 12 Apr 2024
Viewed by 1037
Abstract
As infectious diseases have a severe impact on the individual survival and competitive ability of host species in grassland communities, competition between relevant species may have different consequences, potentially influencing the species composition of grassland communities and the functioning of grassland ecosystems. Understanding [...] Read more.
As infectious diseases have a severe impact on the individual survival and competitive ability of host species in grassland communities, competition between relevant species may have different consequences, potentially influencing the species composition of grassland communities and the functioning of grassland ecosystems. Understanding the impact of infectious diseases on competition is thus crucial for the health management of grassland ecosystems. How do infectious diseases affect the competitive coexistence of grassland plant species? In this study, by drawing on Tilman’s multispecies competition model and incorporating the spread characteristics of grassland plant diseases, we built three spatial competition models of two grass species subject to infectious diseases, and we analyzed the invasion conditions of infectious diseases and how they impact the population dynamics and competitive consequences of the species. Our model revealed the following: (1) Diseases with high transmission rates and low virulence are more likely to invade populations, while the presence of non-host species is detrimental to disease invasion. (2) Disease promotes the coexistence of competing species, breaking down the original competition–compromise trade-off mechanism for species coexistence and greatly expanding the range of parameters within which the two species can coexist. (3) Pathogen infections indirectly weaken the suppression of inferior species by dominant species, which is similar to the cascade effect seen in trophic interactions. Our findings highlight the importance of disease in species coexistence and grassland biodiversity maintenance. Full article
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Figure 1
<p>Thresholds for disease to invade host populations. <math display="inline"><semantics> <mrow> <msubsup> <mi>R</mi> <mn>0</mn> <mn>1</mn> </msubsup> </mrow> </semantics></math> = <math display="inline"><semantics> <mrow> <msubsup> <mi>R</mi> <mn>0</mn> <mn>2</mn> </msubsup> </mrow> </semantics></math> is the invasion threshold for pathogens under Type I and Type II transmission modes, <math display="inline"><semantics> <mrow> <msubsup> <mi>R</mi> <mn>0</mn> <mrow> <mn>31</mn> </mrow> </msubsup> </mrow> </semantics></math> is the invasion threshold when the initial population consists of only the host under Type III transmission mode, and <math display="inline"><semantics> <mrow> <msubsup> <mi>R</mi> <mn>0</mn> <mrow> <mn>32</mn> </mrow> </msubsup> </mrow> </semantics></math> is when the host and its opponent coexist under Type III transmission mode. The value of the parameter above the surface, <math display="inline"><semantics> <mrow> <msub> <mi>R</mi> <mn>0</mn> </msub> <mo>=</mo> <mn>1</mn> </mrow> </semantics></math>, ensures successful invasion; otherwise, invasion fails. Parameters: <math display="inline"><semantics> <mrow> <msub> <mi>c</mi> <mn>1</mn> </msub> <mo>=</mo> <mn>0.6</mn> <mo>,</mo> <msub> <mi>m</mi> <mn>1</mn> </msub> <mo>=</mo> <mn>0.48</mn> <mo>,</mo> <mi>c</mi> <mo>=</mo> <mn>0.45</mn> <mo>,</mo> <msub> <mi>c</mi> <mn>2</mn> </msub> <mo>=</mo> <mn>0.6</mn> <mo>,</mo> <msub> <mi>m</mi> <mn>2</mn> </msub> <mo>=</mo> <mn>0.05</mn> </mrow> </semantics></math>.</p>
Full article ">Figure 2
<p>The impact of infectious diseases on the competitive dynamics of two species in a state of coexistence (subfigures <b>A</b>,<b>C</b>,<b>E</b>) or exclusion (subfigures <b>B</b>,<b>D</b>,<b>F</b>) in Type I, Type II, and Type III models. The graph displays the densities of the superior, infected, and inferior competitors with blue, red, and green lines, respectively. The yellow dashed line represents the sum of the densities of all three groups, and the vertical dashed line indicates the time of infectious disease occurrence in the population. The parameter in the left column is <math display="inline"><semantics> <mrow> <msub> <mi>c</mi> <mn>2</mn> </msub> <mo>=</mo> <mn>0.6</mn> </mrow> </semantics></math>; the parameter in the right column is <math display="inline"><semantics> <mrow> <msub> <mi>c</mi> <mn>2</mn> </msub> <mo>=</mo> <mn>0.4</mn> </mrow> </semantics></math>; and the other parameters are taken identically as <span class="html-italic">c</span><sub>1</sub> = 0.6, <span class="html-italic">m</span><sub>1</sub> = 0.4, <span class="html-italic">m</span><sub>2</sub> = 0.1, <span class="html-italic">β</span> = 3, <span class="html-italic">d</span> = 0.1; additionally, <math display="inline"><semantics> <mrow> <mi>δ</mi> <mo>=</mo> <mn>0.75</mn> </mrow> </semantics></math> is taken for (<b>C</b>,<b>D</b>), and <math display="inline"><semantics> <mrow> <mi>c</mi> <mo>=</mo> <mn>0.4</mn> </mrow> </semantics></math> is taken for (<b>E</b>,<b>F</b>), with initial values of <math display="inline"><semantics> <mrow> <msub> <mi>P</mi> <mn>1</mn> </msub> <mo>,</mo> <msub> <mi>P</mi> <mn>2</mn> </msub> <mo>,</mo> <mi>I</mi> </mrow> </semantics></math> being <math display="inline"><semantics> <mrow> <mrow> <mo>(</mo> <mrow> <mn>0.01</mn> <mo>,</mo> <mo> </mo> <mn>0.001</mn> <mo>,</mo> <mo> </mo> <mn>0.01</mn> </mrow> <mo>)</mo> </mrow> </mrow> </semantics></math>. Some parameter values are taken from Reference [<a href="#B26-diversity-16-00231" class="html-bibr">26</a>].</p>
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<p>Combined effect of transmission rate and toxicity on species coexistence under Type I (<b>a</b>), Type II (<b>b</b>), and Type III (<b>c</b>) modes of transmission. Parameters: <math display="inline"><semantics> <mrow> <msub> <mi>c</mi> <mn>1</mn> </msub> <mo>=</mo> <mn>0.6</mn> <mo>,</mo> <msub> <mi>m</mi> <mn>1</mn> </msub> <mo>=</mo> <mn>0.4</mn> <mo>,</mo> <msub> <mi>c</mi> <mn>2</mn> </msub> <mo>=</mo> <mn>0.4</mn> <mo>,</mo> <msub> <mi>m</mi> <mn>2</mn> </msub> <mo>=</mo> <mn>0.1</mn> <mo>,</mo> <mi>δ</mi> <mo>=</mo> <mn>0.5</mn> <mo>,</mo> <mrow> <mi>and</mi> <mtext> </mtext> </mrow> <mi>c</mi> <mo>=</mo> <mn>0.4</mn> </mrow> </semantics></math>.</p>
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<p>Panel (<b>A</b>) shows the effect of <math display="inline"><semantics> <mi>δ</mi> </semantics></math> on the equilibrium state of system 2. Parameters are <math display="inline"><semantics> <mrow> <msub> <mi>c</mi> <mn>1</mn> </msub> <mo>=</mo> <mn>0.6</mn> <mo>,</mo> <msub> <mi>m</mi> <mn>1</mn> </msub> <mo>=</mo> <mn>0.4</mn> <mo>,</mo> <msub> <mi>c</mi> <mn>2</mn> </msub> <mo>=</mo> <mn>0.35</mn> <mo>,</mo> <msub> <mi>m</mi> <mn>2</mn> </msub> <mo>=</mo> <mn>0.1</mn> <mo>,</mo> <mi>β</mi> <mo>=</mo> <mn>1.8</mn> <mo>,</mo> <mrow> <mtext> </mtext> <mi>and</mi> <mtext> </mtext> </mrow> <mi>d</mi> <mo>=</mo> <mn>0.01</mn> <mo>,</mo> </mrow> </semantics></math> with the same initial values as in <a href="#diversity-16-00231-f002" class="html-fig">Figure 2</a>. Panel (<b>B</b>) shows the effect of <math display="inline"><semantics> <mi>c</mi> </semantics></math> on the equilibrium state of system 3. Parameters are <math display="inline"><semantics> <mrow> <msub> <mi>c</mi> <mn>1</mn> </msub> <mo>=</mo> <mn>0.6</mn> <mo>,</mo> <msub> <mi>m</mi> <mn>1</mn> </msub> <mo>=</mo> <mn>0.4</mn> <mo>,</mo> <msub> <mi>c</mi> <mn>2</mn> </msub> <mo>=</mo> <mn>0.3</mn> <mo>,</mo> <msub> <mi>m</mi> <mn>2</mn> </msub> <mo>=</mo> <mn>0.1</mn> <mo>,</mo> <mi>β</mi> <mo>=</mo> <mn>1.2</mn> <mo>,</mo> <mi>d</mi> <mo>=</mo> <mn>0.05</mn> <mo>,</mo> </mrow> </semantics></math> with the same initial values as in <a href="#diversity-16-00231-f002" class="html-fig">Figure 2</a>. Note that <math display="inline"><semantics> <mrow> <mi>c</mi> <mo>&lt;</mo> <msub> <mi>c</mi> <mn>1</mn> </msub> </mrow> </semantics></math>.</p>
Full article ">Figure 5
<p>Impact of disease on invasion of inferior species under Type I mode of transmission. The black dashed line represents the equal colonization rate of the two species, i.e., <math display="inline"><semantics> <mrow> <msub> <mi>c</mi> <mn>1</mn> </msub> <mo>=</mo> <msub> <mi>c</mi> <mn>2</mn> </msub> </mrow> </semantics></math>. The left side of the magenta line indicates that the inferior species can invade the superior species without disease, where <math display="inline"><semantics> <mrow> <msub> <mi>c</mi> <mn>2</mn> </msub> <mo>&gt;</mo> <msub> <mi>c</mi> <mn>1</mn> </msub> </mrow> </semantics></math> in the light gray area, and <math display="inline"><semantics> <mrow> <msub> <mi>c</mi> <mn>2</mn> </msub> <mo>&lt;</mo> <msub> <mi>c</mi> <mn>1</mn> </msub> </mrow> </semantics></math> in the white gray area; the right indicates that the dominant species invaded the infected inferior species, where <math display="inline"><semantics> <mrow> <msub> <mi>c</mi> <mn>2</mn> </msub> <mo>&gt;</mo> <msub> <mi>c</mi> <mn>1</mn> </msub> </mrow> </semantics></math> in the gray area, and <math display="inline"><semantics> <mrow> <msub> <mi>c</mi> <mn>2</mn> </msub> <mo>&lt;</mo> <msub> <mi>c</mi> <mn>1</mn> </msub> </mrow> </semantics></math> in the dark gray area. The parameters of the first line are <math display="inline"><semantics> <mrow> <msub> <mi>m</mi> <mn>1</mn> </msub> <mo>=</mo> <msub> <mi>m</mi> <mn>2</mn> </msub> <mo>=</mo> <mn>0.4</mn> <mo>,</mo> <mi>d</mi> <mo>=</mo> <mn>0.1</mn> </mrow> </semantics></math>; those of the second line are <math display="inline"><semantics> <mrow> <msub> <mi>m</mi> <mn>1</mn> </msub> <mo>=</mo> <mn>0.3</mn> <mo>,</mo> <msub> <mi>m</mi> <mn>2</mn> </msub> <mo>=</mo> <mn>0.4</mn> </mrow> </semantics></math>; and those of the third line are <math display="inline"><semantics> <mrow> <msub> <mi>m</mi> <mn>1</mn> </msub> <mo>=</mo> <mn>0.4</mn> <mo>,</mo> <msub> <mi>m</mi> <mn>2</mn> </msub> <mo>=</mo> <mn>0.1</mn> </mrow> </semantics></math>.</p>
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11 pages, 1175 KiB  
Article
Comparative Prevalence and Intensity of Endoparasites in a Dynamic Boreal Ungulate Community
by Cassandra L. Andrew, Brent Wagner, N. Jane Harms, Emily J. Jenkins and Thomas S. Jung
Diversity 2024, 16(4), 230; https://doi.org/10.3390/d16040230 - 12 Apr 2024
Cited by 1 | Viewed by 1287
Abstract
Surveillance of endoparasites at the host community level is rarely reported for ungulates. Yet, changes in the composition and abundance of species in ungulate assemblages, coupled with environmental and climate change, bring into focus the need for baseline data on endoparasite occurrence in [...] Read more.
Surveillance of endoparasites at the host community level is rarely reported for ungulates. Yet, changes in the composition and abundance of species in ungulate assemblages, coupled with environmental and climate change, bring into focus the need for baseline data on endoparasite occurrence in host species at the community level. We investigated the prevalence and intensity of eggs of endoparasites in feces of a dynamic boreal ungulate community in Yukon, Canada, that included reintroduced bison (Bison bison), as well as introduced elk (Cervus canadensis), naturally colonizing mule deer (Odocoileus hemionus), and resident populations of caribou (Rangifer tarandus), moose (Alces americanus), and thinhorn sheep (Ovis dalli). We also examined the change in endoparasite prevalence and intensity in bison fecal samples collected eight years apart. The prevalence of eggs detected in feces differed across species for most endoparasite groups. We also provide new records of several endoparasites in novel hosts or new geographic records. We detected a substantially greater prevalence and intensity of trichostrongyle-type eggs in bison feces between samples collected eight years apart. Our data emphasize the need for targeted pathogen surveillance programs to monitor the movement of various ungulate and associated endoparasites. This is particularly pertinent since our data potentially supports evidence for the continued northward expansion and host switching of protostrongylid species, which may have health implications for animals at a new interface. Full article
(This article belongs to the Section Animal Diversity)
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<p>Locations where ungulate fecal samples were collected by species in Yukon, Canada.</p>
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<p>Example of spike-tailed protostrongylid first-stage larvae (L1), most likely <span class="html-italic">Protostrongylus stilesi</span> in thinhorn sheep (<span class="html-italic">Ovis dalli</span>) or <span class="html-italic">Orthostrongylus macrotis</span> in cervids.</p>
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17 pages, 2951 KiB  
Article
Habitat Selection of Three Neotropical Grassland Birds Is Dependent on Vegetation Structure and Resources
by Jo Peacock, Ross Macleod, G. Matt Davies, Tjalle Boorsma and Christopher M. Tonra
Diversity 2024, 16(4), 229; https://doi.org/10.3390/d16040229 - 10 Apr 2024
Viewed by 1338
Abstract
Grassland birds are globally imperiled. Those of endemic Neotropical savannas may be particularly threatened as knowledge of the ecology of many species is lacking, restricting our ability to take decisive conservation action. During the dry (non-breeding) season of 2010, we studied the population [...] Read more.
Grassland birds are globally imperiled. Those of endemic Neotropical savannas may be particularly threatened as knowledge of the ecology of many species is lacking, restricting our ability to take decisive conservation action. During the dry (non-breeding) season of 2010, we studied the population size, distribution, and habitat associations of the Cock-tailed Tyrant (Alectrurus tricolor), Black-masked Finch (Coryphaspiza melanotis), and Wedge-tailed Grass-finch (Emberiziodes herbicola) across a disturbance-mediated savanna–grassland gradient in Beni, Bolivia. We used distance sampling and surveyed structural and resource-specific habitat features at plots where birds were present versus random locations. Occupancy models identified fine-scale habitat associations. Cock-tailed Tyrant (7.1 ind./km2) specialized on open habitats in areas expected to be heavily inundated in the wet season, avoided trees, and selected tall grassy swards. Black-masked Finch (25.1 ind./km2) occurred across the gradient, associating with tall, forb-rich swards, sparse shrubs, and low levels of fruiting and seeding vegetation. Wedge-tailed Grass-finch (27.9 ind./km2) also occurred across the gradient, particularly associated with tall, forb-rich swards, abundant seeding grasses, and sparse shrubs. Our results offer the first quantitative abundance estimates for these species in Beni, provide vital baselines for future monitoring, and improve knowledge of the ecology and conservation management needs of these species. Importantly, our results suggest that populations of these three grassland birds may be best maintained in heterogenous, mosaic landscapes that can be produced by carefully managed burning and grazing. Further research in the breeding season would facilitate making stronger, more specific management recommendations. Full article
(This article belongs to the Special Issue Avian Diversity in Forest and Grassland)
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<p>Results of the Principal Component Analysis showing PC1: Floodplain gradient (a +ve score on this axis indicates a preference for areas of the floodplain that are heavily inundated during the wet season) plotted against (<b>A</b>) PC2: Forb-rich seeding gradient (a −ve score on this axis indicates a preference for forb-rich grassland with abundant seeding/fruiting forbs and shrubs); (<b>B</b>) PC3: Tall seeding grassland gradient (a +ve score on this axis indicates a preference for tall grassland or grassland with abundant seeding grasses); (<b>C</b>) PC4: Openness gradient (a +ve score on this axis indicates a preference for more densely wooded grassland); (<b>D</b>) PC5: Woody shrub gradient (a +ve score on this axis indicates a preference for grassland with abundant woody shrubs). See Results for detailed descriptions of each PC axis. Ellipses represent centroid values for each species and their standard deviation from the mean.</p>
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<p>Forest plots showing results from occupancy modeling for (<b>A</b>) Cock-tailed Tyrant; (<b>B</b>) Black-masked Finch; and (<b>C</b>) Wedge-tailed Grass-finch. For (<b>B</b>,<b>C</b>), (i) shows the continuous variables from the model and (ii) shows the categorical variables. Note differences in scale for odds ratios used in (i) versus (ii). Dots show point estimates for each variable. Lines are 95% confidence intervals (95% CI). Variables with 95% CIs overlapping 1 are non-significant; variables with 95% CIs that do overlap 0 are significant. Estimates &gt; 1 represent a positive effect of the variable, and estimates &lt; 1 a negative effect. The abundance of categorical variables is shown as low, medium, and high as data were ordinal (see Methods for details).</p>
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<p>Effects plots from occupancy modeling for Cock-tailed Tyrants (<b>A</b>,<b>B</b>), Black-masked Finch (<b>C</b>,<b>D</b>), and Wedge-tailed Grass-finch (<b>E</b>,<b>F</b>). Plots visualize the predicted probability of occupancy as a function of significant model variables. For Black-masked Finch and Wedge-tailed Grass-finch plots D and F are distinguished from C and E by the presence of low levels of woody shrubs.</p>
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13 pages, 1492 KiB  
Article
Genetic Variation in the Pallas’s Cat (Otocolobus manul) in Zoo-Managed and Wild Populations
by Joshua J. Robinson, Alexis D. Crichlow, Charlotte E. Hacker, Bariushaa Munkhtsog, Bayaraa Munkhtsog, Yuguang Zhang, William F. Swanson, Leslie A. Lyons and Jan E. Janecka
Diversity 2024, 16(4), 228; https://doi.org/10.3390/d16040228 - 10 Apr 2024
Viewed by 1443
Abstract
The Pallas’s cat (Otocolobus manul) is one of the most understudied taxa in the Felidae family. The species is currently assessed as being of “Least Concern” in the IUCN Red List, but this assessment is based on incomplete data. Additional ecological [...] Read more.
The Pallas’s cat (Otocolobus manul) is one of the most understudied taxa in the Felidae family. The species is currently assessed as being of “Least Concern” in the IUCN Red List, but this assessment is based on incomplete data. Additional ecological and genetic information is necessary for the long-term in situ and ex situ conservation of this species. We identified 29 microsatellite loci with sufficient diversity to enable studies into the individual identification, population structure, and phylogeography of Pallas’s cats. These microsatellites were genotyped on six wild Pallas’s cats from the Tibet Autonomous Region and Mongolia and ten cats from a United States zoo-managed population that originated in Russia and Mongolia. Additionally, we examined diversity in a 91 bp segment of the mitochondrial 12S ribosomal RNA (MT-RNR1) locus and a hypoxia-related gene, endothelial PAS domain protein 1 (EPAS1). Based on the microsatellite and MT-RNR1 loci, we established that the Pallas’s cat displays moderate genetic diversity. Intriguingly, we found that the Pallas’s cats had one unique nonsynonymous substitution in EPAS1 not present in snow leopards (Panthera uncia) or domestic cats (Felis catus). The analysis of the zoo-managed population indicated reduced genetic diversity compared to wild individuals. The genetic information from this study is a valuable resource for future research into and the conservation of the Pallas’s cat. Full article
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<p>Sampling sites for the Pallas’s cat (<span class="html-italic">Otocolobus manul</span>) scats included in this study. Scats were collected in Shenza, Tibet Autonomous Region (<span class="html-italic">n</span> = 1) and the Western and Eastern Beauties of Mongolia (<span class="html-italic">n</span> = 2 and <span class="html-italic">n</span> = 3, respectively) during noninvasive genetic surveys.</p>
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<p>Minimum spanning network of Pallas’s cats (<span class="html-italic">Otocolobus manul</span>) at the mitochondrial <span class="html-italic">12S ribosomal RNA</span> (MT-<span class="html-italic">RNR1</span>; 91 bp) locus. Sequences originated from six wild and ten zoo-managed cats sequenced in this study and six additional sequences from NCBI’s GenBank (<span class="html-italic">n</span> = 22). The wild Pallas’s cat scats were collected in Shenza, Tibet Autonomous Region (<span class="html-italic">n</span> = 1) and the Western and Eastern Beauties of Mongolia (<span class="html-italic">n</span> = 2 and <span class="html-italic">n</span> = 3, respectively). The white, gray, and black coloration of the haplotypes correspond to zoo-managed, wild, and GenBank individuals, respectively. Shared haplotypes are split proportionally based on the number of sequences collected from wild specimens, zoo-managed specimens, or sequences available through GenBank. Each solid branch represents one mutational step between haplotypes. For each haplotype, the nucleotide present at each segregating site is listed above.</p>
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<p>Haplotype of the translated <span class="html-italic">endothelial PAS domain protein 1</span> (<span class="html-italic">EPAS1</span>) product identified in ten Pallas’s cats (<span class="html-italic">Otocolobus manul</span>) housed in AZA-accredited zoos and three wild Pallas’s cats from the Eastern Beauty of Mongolia. Both loci were independently sequenced and compared to translated sequences from the domestic cat (<span class="html-italic">Felis catus</span>), tiger (<span class="html-italic">Panthera tigris</span>), and snow leopard (<span class="html-italic">Panthera uncia</span>), which were previously collected by [<a href="#B19-diversity-16-00228" class="html-bibr">19</a>]. The outlined box highlights the unique substitution observed in the Pallas’s cat for this gene. Exon and residue numbers are based on human orthologs.</p>
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16 pages, 5161 KiB  
Article
Exploring Morphological Population Variability: Host Plant and Habitat Dependency in the Protected Moth Gortyna borelii (Lepidoptera, Noctuidae)
by László Rákosy, Mihai Alexandru Martin, Geanina Magdalena Sitar, Andrei Crișan and Cristian Sitar
Diversity 2024, 16(4), 227; https://doi.org/10.3390/d16040227 - 9 Apr 2024
Viewed by 1869
Abstract
In this paper, we discuss the evolutionary implications of the correlation between different species of Peucedanum plants and the distribution of Gortyna borelii moth populations in Romania. We highlight geographic separation and isolation among these populations due to anthropogenic landscape fragmentation, which hinders [...] Read more.
In this paper, we discuss the evolutionary implications of the correlation between different species of Peucedanum plants and the distribution of Gortyna borelii moth populations in Romania. We highlight geographic separation and isolation among these populations due to anthropogenic landscape fragmentation, which hinders genetic exchange. A geometric morphometric analysis was utilized to visualize and compare the morphometric variations in relation to the environmental variables, particularly the host plant. Additionally, the distribution of G. borelii populations across Europe and in Romania that are correlated with the host plant was analyzed. The significant morphological and morphometric differences between the analyzed populations support our working hypothesis, according to which the use of different Peucedanum species by the larvae of G. borelii leads to an intraspecific diversification correlated with the host plant species. The newly discovered population of G. borelii in Romania holds substantial conservation importance, necessitating protection measures, including demarcating habitat areas and raising awareness among stakeholders. G. borelii is a protected species at the European level (Habitats Directive 92/43/EEC, Appendices II and IV), considered endangered due to the isolation of its populations and anthropogenic pressures exerted through agricultural practices. Understanding the impact of agricultural practices on their habitat is crucial for effective management strategies. Overall, this study sheds light on the complex interplay between ecological adaptation, host plant specialization, and speciation dynamics in phytophagous insects, emphasizing the importance of conservation efforts to preserve G. borelii populations and their habitats. Full article
(This article belongs to the Special Issue Speciation, Phylogenetics and Taxonomy of Lepidoptera)
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<p>(<b>A</b>) <span class="html-italic">Gortyna borelli</span> from Viișoara; (<b>B</b>) <span class="html-italic">Gortyna borelii</span> from newly discovered site near Aphida; (<b>C</b>) the species’ habitat in Cefa; (<b>D</b>) the species’ habitat in Viișoara; (<b>E</b>) the species’ habitat in Apahida; (<b>F</b>) the species’ habitat in the Domogled Mountain.</p>
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<p>Specimens of <span class="html-italic">G. borelii</span> from study sites: (<b>A</b>) Apahida, (<b>B</b>) Viișoara, and (<b>C</b>) Cefa (Crișana).</p>
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<p>Landmarks selected for geometric morphometrics and linear measurements.</p>
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<p>(<b>A</b>) Distribution of <span class="html-italic">Gortyna borelii</span> in Europe (adapted from [<a href="#B10-diversity-16-00227" class="html-bibr">10</a>,<a href="#B67-diversity-16-00227" class="html-bibr">67</a>], modified and corrected), indicating <span class="html-italic">Peucedanum</span> species specific to the larvae in various geographical regions. Circles represent records prior to 1980, while black dots represent records after 1980; (<b>B</b>) records of <span class="html-italic">Gortyna borelii</span> from Romania are provided, along with indications of <span class="html-italic">Peucedanum</span> species on which its larvae feed in different geographical areas.</p>
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<p>Graphic representation of Procrustes fit results.</p>
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<p>Graphic representation of Principal Component 1 for each landmark.</p>
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<p>Graphic representation of Principal Component 2 for each landmark.</p>
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<p>PCA1 and PC2 for all individuals in the study, with Confidence Ellipses for means at a 90% probability. Red-Apahida, green-Cefa, and blue-Viișoara.</p>
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<p>Canonical Variance Analysis for all individuals in the analysis, with Confidence Ellipses for means at a 90% probability. Red-Apahida, green-Cefa, and blue-Viișoara.</p>
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7 pages, 1766 KiB  
Interesting Images
Large-Scale Re-Implantation Efforts for Posidonia oceanica Restoration in the Ligurian Sea: Progress and Challenges
by Chiara Robello, Stefano Acunto, Laura Marianna Leone, Ilaria Mancini, Alice Oprandi and Monica Montefalcone
Diversity 2024, 16(4), 226; https://doi.org/10.3390/d16040226 - 9 Apr 2024
Cited by 1 | Viewed by 1835
Abstract
The Ligurian Sea (NW Mediterranean) has been a focal point for numerous interventions aimed at restoring Posidonia oceanica meadows. The success of pioneer restoration actions in France during the 1970s stimulated similar initiatives across the Mediterranean Sea. Early attempts in the Ligurian Sea [...] Read more.
The Ligurian Sea (NW Mediterranean) has been a focal point for numerous interventions aimed at restoring Posidonia oceanica meadows. The success of pioneer restoration actions in France during the 1970s stimulated similar initiatives across the Mediterranean Sea. Early attempts in the Ligurian Sea were implemented in 1993 and 1996 on limited seabed areas (i.e., tens of square meters) at the two coastal sites of Sori and Rapallo (Liguria, NW Italy). No further initiatives have been reported for the Ligurian Sea until 2022. In that year, a large-scale restoration project, which uses biodegradable mats coupled with metal mesh, began in Liguria. Different levels of anthropogenic pressure and wave exposure characterize the three investigated locations: (1) Portofino, on the eastern Liguria and on the border with the Portofino Marine Protected Area; (2) Bergeggi in the central Liguria and within the Isola di Bergeggi Marine Protected Area; and (3) Sanremo in the western Liguria, without any formal protection. Despite recent setbacks caused by severe storms in late 2023, which particularly damaged the Portofino site, ongoing monitoring revealed promising survival rates. Most notably, the site in Bergeggi displayed a 90% survival rate in September 2023. Although challenges to restore P. oceanica beds persist, such as mitigating damages caused by unpredictable events, this extensive re-implantation initiative offers the opportunity to evaluate the effectiveness of new basin-scale restoration strategies. This approach marks an important step in the conservation of Posidonia oceanica habitat. Full article
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<p><span class="html-italic">Posidonia oceanica</span> restoration sites in Liguria (NW Italy). Historical sites are marked with dots; the new re-implantation sites are marked with stars.</p>
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<p>(<b>a</b>) Scientific diver involved in planting cuttings at the early phase of the re-implantation. (<b>b</b>) Overhead view of two out of ten re-implanted biomats.</p>
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38 pages, 4089 KiB  
Review
The Fossil Record and Diversity of Pycnodontiform Fishes in Non-Marine Environments
by John J. Cawley and Jürgen Kriwet
Diversity 2024, 16(4), 225; https://doi.org/10.3390/d16040225 - 9 Apr 2024
Viewed by 3633
Abstract
Pycnodont fishes were a successful clade of neopterygian fishes that are predominantly found in shallow marine deposits. However, throughout their long 180 million year reign (Late Triassic–end Eocene), they made multiple incursions into both brackish and freshwater environments. This fossil record mostly consists [...] Read more.
Pycnodont fishes were a successful clade of neopterygian fishes that are predominantly found in shallow marine deposits. However, throughout their long 180 million year reign (Late Triassic–end Eocene), they made multiple incursions into both brackish and freshwater environments. This fossil record mostly consists of fragmentary dental material, but articulated specimens are known from Early Cretaceous lacustrine localities in Spain. This review article aims to document all non-marine occurrences of Pycnodontiformes throughout most of the Mesozoic and early Paleogene. This review highlights two interesting trends in the history of non-marine habitat colonization by pycnodonts: (1) a huge spike in non-marine occurrences during the Cretaceous; and (2) that most occurrences in non-marine localities occurred at the latest Cretaceous period, the Maastrichtian. The high number of colonization events within the Cretaceous lines up with extreme climatic events, such as high temperatures resulting in high sea levels which regularly flooded continental masses, allowing pycnodonts easier access to non-marine habitats. The increased presence of pycnodonts in brackish and freshwater habitats during the Maastrichtian might have played a role in their survival through the K/Pg extinction event. Freshwater habitats are not as vulnerable as marine ecosystems to environmental disturbance as the base of their food chain relies on detritus. Pycnodonts might have used such environments as a refuge and began to occupy marine waters after the K/Pg extinction event. Full article
(This article belongs to the Special Issue Diversity, Biogeography and Evolution of Actinopterygians)
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<p>Holotype of <span class="html-italic">Ocloedus subdiscus</span> (MNHN MSE 301G) from the Early Cretaceous (Berriasian–Valanginian) El Montsec, Spain. This species represents one of the few articulated specimens of a pycnodont from a freshwater environment. Collection abbreviations: MNHN—Muséum national d’Histoire naturelle, Paris. Scale bar is 10 mm.</p>
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<p>Examples of jaw fragments of pycnodont taxa from non-marine localities. (<b>A</b>) cf. <span class="html-italic">Coelodus</span> sp. (MTM V 2010.139.1). (<b>B</b>) Pycnodontiformes incertae sedis (UFRJ-DG 423-PD). (<b>C</b>) <span class="html-italic">Agassizilia erfoudina</span> (FSAC-KK 5073). (<b>D</b>) <span class="html-italic">Neoproscinetes africanus</span> (FSAC-KK 5070). (<b>E</b>) <span class="html-italic">Turbomesodon</span> cf. <span class="html-italic">arcuatus</span> (NHM PV P.45763). Collection abbreviations: FSAC—Faculté des Sciences Aïn Chock; MTM—Hungarian Natural History Museum (Magyar Természettudományi Múzeum); NHM—Natural History Museum, London; UFRJ—Universidade Federal do Rio de Janeiro. Figures of <span class="html-italic">Turbomesodon</span> cf. <span class="html-italic">arcuatus</span>, <span class="html-italic"> Neoproscinetes africanus</span>, <span class="html-italic">Agassizilia erfoudinia</span>, Pycnodontiformes incertae sedis and <span class="html-italic">Coelodus</span> sp. modified from [<a href="#B29-diversity-16-00225" class="html-bibr">29</a>,<a href="#B47-diversity-16-00225" class="html-bibr">47</a>,<a href="#B151-diversity-16-00225" class="html-bibr">151</a>,<a href="#B200-diversity-16-00225" class="html-bibr">200</a>] respectively. Scale bar for (<b>A</b>,<b>C</b>–<b>E</b>) is 10 mm. Scale bar for (<b>B</b>) is 5 mm.</p>
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<p>Paleobiogeographic distribution of non-marine pycnodonts through time. Numbered stars refer primarily to geological age. When geological age is unclear, the star will represent the locality the fossil was collected from as well as the currently time span that the locality is believed to represent. All cited localities and localities referring to a particular stage are discussed in further detail within the main text. Maps modified from Scotese [<a href="#B252-diversity-16-00225" class="html-bibr">252</a>,<a href="#B253-diversity-16-00225" class="html-bibr">253</a>,<a href="#B254-diversity-16-00225" class="html-bibr">254</a>,<a href="#B255-diversity-16-00225" class="html-bibr">255</a>]. (<b>A</b>) Late Jurassic, Oxfordian, 158.4 Ma: 1. Changtu, Tibet, Late Jurassic; 2. Khlong Min Formation, Thailand, Mid–Late Jurassic; 3. Morrison Formation, USA, Oxfordian–Tithonian; 4. Mugher Mudstone, Ethiopia, ?Kimmeridgian–Tithonian; 5. Stanleyville Formation, Democratic Republic of Congo, Kimmeridgian–Valanginian. (<b>B</b>) Early Cretaceous, early Aptian, 121.8 Ma: 1. Berriasian; 2. Iberian Basin, eastern Spain, Berriasian–Valanginian, Barremian–Albian; 3. Southern England, Berriasian–Valanginian, Hauterivian–Barremian; 4. Valanginian 5. Phu Phan Thong, Thailand, Hauterivian–Barremian; 6. Vega de Pas Formation, northern Spain, Hauterivian–Barremian; 7. Bernissart, Belgium, Barremian–Aptian; 8. Paluxy Formation, northern Texas, USA, Albian–Aptian; 9. Aptian; 10. Albian; 11. Kem Kem, Albian–Cenomanian. (<b>C</b>) Late Cretaceous, Maastrichtian, 68 Ma: 1. Cenomanian; 2. Turonian; 3. Southern Utah, USA, Turonian–Campanian; 4. Donggou Formation, China, Coniacian–Campanian; 5. Santonian; 6. Campanian; 7. Lo Hueco (Cuenca), Spain, Campanian–Maastrichtian; 8. Maastrichtian; 9. Jhilmili, India, Maastrichtian–Danian; 10. Rajasthan, India, Maastrichtian–Selandian. (<b>D</b>) Paleogene, Ypresian, 52.2 Ma: 1. Danian; 2. Teberemt and Tamaguélelt Formations, Mali, Selandian–Ypresian; 3. Lutetian.</p>
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<p>Distribution of non-marine habitat transitions throughout a time-calibrated phylogeny of Pycnodontiformes based on work by Ebert [<a href="#B124-diversity-16-00225" class="html-bibr">124</a>]. The green vertical line represents the K/Pg boundary. Freshwater and brackish environments are represented by blue and red bars, respectively. Branches which contain both red and blue bars indicate the occupation of both environments by that taxon during that particular geological stage. Uppercase letters at certain nodes represent monophyletic groups: A: Pycnodontiformes; B: Mesturidae; C: Brembodontidae; D: Pycnodontidae; E: Proscinetinae; * represents indeterminate position of <span class="html-italic">Anomoeodus</span> within Pycnodontidae based on a previous phylogenetic analysis [<a href="#B48-diversity-16-00225" class="html-bibr">48</a>]. Geological ages are represented by abbreviations which are listed here in chronological order: In, Induan; Ol, Olenkian; Ani, Anisian; Lad, Ladinian; Carn, Carnian; Nor, Norian; Rha, Rhaetian; H, Hettangian; Sin, Sinemurian; Pli, Pliensbachian; Toa, Toarcian; Aal, Aalenian; Baj, Bajocian; Bt, Bathonian; Cal, Callovian; Ox, Oxfordian; Kim, Kimmeridgian; Ti, Tithonian; Ber, Berriasian; Val, Valanginian; Hau, Hauterivian; Bar, Barremian; Apt; Aptian; Alb, Albian; Cen; Cenomanian; Tur, Turonian; Con, Coniacian; S, Santonian; Camp, Campanian; Maas, Maastrichtian; Dan, Danian; Se, Selandian; Th, Thanetian; Ypr, Ypresian; Lut, Lutetian. Figure produced with TSCreator (<a href="https://timescalecreator.org/" target="_blank">https://timescalecreator.org/</a>, accessed 19 March 2024).</p>
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<p>Total number of non-marine pycnodont occurrences from each geological stage of the Cretaceous.</p>
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15 pages, 4470 KiB  
Article
Dissimilarity among Species and Higher Taxa of Amphibians in a Hotspot of Biodiversity and Endemism in the Neotropics
by Jaime Manuel Calderón-Patrón, Karen Elizabeth Peña-Joya, Jorge Téllez-López and Eréndira Patricia Canales-Gómez
Diversity 2024, 16(4), 224; https://doi.org/10.3390/d16040224 - 9 Apr 2024
Viewed by 1750
Abstract
The Mexican Republic ranks fifth in the world in terms of amphibian diversity, and within Mexico, the state of Oaxaca has the greatest amphibian richness and endemism. Unfortunately, various factors, such as land use change and global warming, have caused a global crisis [...] Read more.
The Mexican Republic ranks fifth in the world in terms of amphibian diversity, and within Mexico, the state of Oaxaca has the greatest amphibian richness and endemism. Unfortunately, various factors, such as land use change and global warming, have caused a global crisis that threatens the conservation of this class. In the face of these threats, an analysis of beta diversity provides information that can be applied to conservation strategies, since its study reveals the spatial scaling of diversity loss and clarifies the mechanisms of regional diversity maintenance. In this work, we analyzed the beta diversity at the species and higher taxa level (order, family, subfamily, genus and species) for the amphibians of Oaxaca and their replacement components and the differences in richness for anurans and caudates separately between physiographic subprovinces. Very high beta diversity was recorded, with higher diversity occurring among caudates (0.92) than among anurans (0.84). Species replacement was the component that most contributed to this result, and the subprovinces with substantial environmental differences had the most dissimilar amphibian communities. The results of this study show the need to implement conservation strategies in subprovinces with high amphibian richness and endemism levels, following the example of Sierra Madre de Oaxaca (SMO), where local communities have developed conservation actions in most of the territory. Full article
(This article belongs to the Section Animal Diversity)
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<p>Map of subprovinces of Oaxaca: Balsas Depression (DB); Mountains and Valleys of the West (MVO); Tehuacán Trench (TT); Sierra Madre de Oaxaca (SMO); Gulf Coastal Plain (PCG); Central Valleys of Oaxaca (VCO); Mountains and Valleys of the Center (MVC); Isthmic Depression of Tehuantepec (DIT); Sierra Madre de Chiapas (SMC); Sierra Madre del Sur (SMS); Pacific Coastal Plain (PCP); and Tehuantepec Coastal Plain (PCT) [<a href="#B2-diversity-16-00224" class="html-bibr">2</a>,<a href="#B11-diversity-16-00224" class="html-bibr">11</a>].</p>
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<p>Total species and taxonomic beta diversity of amphibians, anurans and caudates among the 12 physiographic subprovinces of the state of Oaxaca. The replacement component contributes more to the total beta diversity of amphibians, both at the species and higher taxa levels. SP = species level; TX = higher taxa level.</p>
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<p>Total beta diversity of species and higher taxa of amphibians, anurans and caudates calculated by pairs of the 12 physiographic subprovinces of the state of Oaxaca. Total beta diversity of species: (<b>A</b>) amphibians, (<b>B</b>) anurans and (<b>C</b>) caudates. Total beta diversity of higher taxa: (<b>D</b>) amphibians, (<b>E</b>) anurans and (<b>F</b>) caudates. SP = species level; TX = higher taxa level.</p>
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<p>NMDS ordination analysis for the total species and taxonomic beta diversity, turnover and differences in richness for amphibians, anurans and caudates (that of caudates is new). (<b>A</b>) Total beta diversity of anuran species, (<b>B</b>) anuran species replacement, (<b>C</b>) differences in anuran species richness, (<b>D</b>) amphibian total taxonomic beta diversity, (<b>E</b>) anuran total taxonomic beta diversity, (<b>F</b>) caudates total taxonomic beta diversity, (<b>G</b>) amphibian replacement of species, (<b>H</b>) anuran replacement of species, (<b>I</b>) caudates replacement of species, (<b>J</b>) amphibian taxonomic replacement, (<b>K</b>) anurans taxonomic replacement and (<b>L</b>) caudate taxonomic replacement.</p>
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<p>Correlations between total beta diversity, turnover and differences in richness for species and higher taxa of all amphibians (<b>A</b>–<b>C</b>), anurans (<b>D</b>–<b>F</b>) and caudates (<b>G</b>–<b>I</b>) from physiographic subprovinces in Oaxaca.</p>
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14 pages, 2534 KiB  
Article
Bears into the Niche-Space: Phylogeography and Phyloclimatic Model of the Family Ursidae
by Carlos Luna-Aranguré and Ella Vázquez-Domínguez
Diversity 2024, 16(4), 223; https://doi.org/10.3390/d16040223 - 8 Apr 2024
Viewed by 2362
Abstract
Assessing niche evolution remains an open question and an actively developing area of study. The family Ursidae consists of eight extant species for which, despite being the most studied family of carnivores, little is known about the influence of climate on their evolutionary [...] Read more.
Assessing niche evolution remains an open question and an actively developing area of study. The family Ursidae consists of eight extant species for which, despite being the most studied family of carnivores, little is known about the influence of climate on their evolutionary history and diversification. We evaluated their evolutionary patterns based on a combined phylogeography and niche modeling approach. We used complete mitogenomes, estimated divergence times, generated ecological niche models and applied a phyloclimatic model to determine the species evolutionary and diversification patterns associated with their respective environmental niches. We inferred the family evolutionary path along the environmental conditions of maximum temperature and minimum precipitation, from around 20 million years ago to the present. Our findings show that the phyloclimatic niches of the bear species occupy most of the environmental space available on the planet, except for the most extreme warm conditions, in accordance with the wide geographic distribution of Ursidae. Moreover, some species exhibit broader environmental niches than others, and in some cases, they explore precipitation axes more extensively than temperature axes or vice versa, suggesting that not all species are equally adaptable to these variables. We were able to elucidate potential patterns of niche conservatism and evolution, as well as niche overlapping, suggesting interspecific competitive exclusion between some of the bear species. We present valuable insights into the ecological and evolutionary processes driving the diversification and distribution of the Ursidae. Our approach also provides essential information for guiding effective conservation strategies, particularly in terms of distribution limits in the face of climate change. Full article
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<p>Geographic distribution of the family Ursidae occurrences, obtained from the scientific literature and global databases. The filtered database includes 126 records of <span class="html-italic">Ailuropoda melanoleuca</span>, 2174 of <span class="html-italic">Tremarctos ornatus</span>, 71 of <span class="html-italic">Melursus ursinus</span>, 35 of <span class="html-italic">Helarctos malayanus</span>, 194 of <span class="html-italic">Ursus thibetanus</span>, 756 of <span class="html-italic">Ursus americanus</span>, 9107 of <span class="html-italic">Ursus arctos</span>, and 559 of <span class="html-italic">Ursus maritimus</span>.</p>
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<p>Ecological niche models based on isotopic methods, showing one-dimensional density plots, two-dimensional scatterplots, and ellipsoids for each species of the family Ursidae. Ellipsoids per species show 20 iterations of estimated niche amplitude and niche overlapping patterns. The temperature values were multiplied by 10 and shown on a Celsius scale. Precipitation values are shown in millimeters of rainfall. The grey color represents the environmental values of 100,000 equidistant random land points from the planet.</p>
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<p>Time-calibrated Bayesian tree in million years, based on complete mitochondrial genomes (15,670 bp) of the eight extant species of the family Ursidae. The red panda <span class="html-italic">Ailurus fulgens</span> was used as an outgroup. The estimated median time and range are indicated for some nodes. All the indicated nodes have a 95% highest posterior density (HPD) equal to one.</p>
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<p>Phyloclimatespace results for the eight extant species of the family Ursidae. The model retains the relationships between the complete mitochondrial sequences of the species (<a href="#diversity-16-00223-f002" class="html-fig">Figure 2</a>), positioning each tip of the tree on the combination of precipitation and temperature of its environmental centroid. It shows linear reconstructions of the ecological trajectories of the ancestors (i.e., the internal nodes of the tree and the root). The niche centroid per species was determined from the environmental data extracted from the occurrence records available in GBIF and the scientific literature, while the ellipsoids were estimated by using 95% of the occurrences.</p>
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