[go: up one dir, main page]
More Web Proxy on the site http://driver.im/
Previous Issue
Volume 5, December
You seem to have javascript disabled. Please note that many of the page functionalities won't work as expected without javascript enabled.
 
 

Ecologies, Volume 6, Issue 1 (March 2025) – 22 articles

  • Issues are regarded as officially published after their release is announced to the table of contents alert mailing list.
  • You may sign up for e-mail alerts to receive table of contents of newly released issues.
  • PDF is the official format for papers published in both, html and pdf forms. To view the papers in pdf format, click on the "PDF Full-text" link, and use the free Adobe Reader to open them.
Order results
Result details
Select all
Export citation of selected articles as:
14 pages, 2940 KiB  
Article
Biodiversity Surveys Before Residential Building Renovations in Bulgaria with Emphasis on the Impact and Conservation of Building-Dwelling Fauna
by Stanimira Deleva, Nikolay Kolev, Angel Ivanov, Pavlina Marinova, Nasko Petkov and Nikolay Natchev
Ecologies 2025, 6(1), 22; https://doi.org/10.3390/ecologies6010022 - 4 Mar 2025
Viewed by 223
Abstract
The urbanization and the expansion of human settlements led to the adaptation of many animal species to living close to humans, often using buildings for roosting. Panel buildings are particularly attractive to rock-dwelling animals such as swifts, swallows, pigeons, and bats due to [...] Read more.
The urbanization and the expansion of human settlements led to the adaptation of many animal species to living close to humans, often using buildings for roosting. Panel buildings are particularly attractive to rock-dwelling animals such as swifts, swallows, pigeons, and bats due to their numerous cracks and crevices. The abundance of these structures in Eastern Europe has led to the establishment of numerous bird and bat colonies in the cities. However, the recent renovation and insulation of these buildings, while beneficial to residents, threatens the roosts. Construction workers are sometimes unaware of animal presence and inadvertently destroy nests or colonies. Rapid assessments before renovation are essential to rescue individuals and ensure the planning of alternative roosts for bats and birds. We conducted a pilot survey of 61 residential buildings in five municipalities in Bulgaria: Razgrad, Popovo, Haskovo, Dimitrovgrad, and Bobov Dol, to assess bird and bat biodiversity. We performed field assessments using direct observation, thermal cameras, ultrasonic detection, sunset counts, and endoscopic cameras. The most commonly detected bird species were the house martin, barn swallow, common swifts, the Eurasian jackdaw, pigeons, and sparrows. The most commonly detected bat species were the common pipistrelle, noctule, and Kuhl’s pipistrelle. Additionally, we discuss the specifics of the “soviet-type” buildings as nesting facilities for pigeons and the impact of the pigeons on the “micro ecology” of the blocks. Our study aimed to guide conservation actions and awareness during the expanding renovation efforts of old buildings in Bulgaria. Full article
Show Figures

Figure 1

Figure 1
<p>Research sites: (<b>a</b>), an example of a “soviet style” panel building; (<b>b</b>), map of Bulgaria with the six municipalities—Razgrad (pink), Popovo (blue), Dimitrovgrad (light green), Haskovo (dark green), and Bobov dol (orange); (<b>c</b>), schematic representation of the characteristics of the buildings, mentioned in the text: red arrow—the section above the last floor and the roof—the “air bag” with its apertures, indicated by green arrow; tan arrow—balcony and façades; pale blue arrow—vertical joints; dark blue—horizontal joints between panels; purple—basements; magenta—chipped plaster.</p>
Full article ">Figure 2
<p>Bats and birds roosting in and around the studied buildings and the location of their observation.</p>
Full article ">Figure 3
<p>Building’s infestation with feral pigeons: (<b>a</b>), nesting pigeons and guano on a balcony; (<b>b</b>), fresh carcass of a pigeon found in the under-roof space; (<b>c</b>), guano accumulations in the under-roof space; (<b>d</b>), reduced carcases of a pigeon in the under-roof space.</p>
Full article ">Figure 4
<p>Figure representing the relation between diversity indices and different building characteristics. The statistically significant values are highlighted with an asterisk.</p>
Full article ">Figure 5
<p>Feral pigeon inhabiting the inspected buildings: (<b>a</b>), pigeon resting on the construction build to frighten birds; (<b>b</b>), courtship of feral pigeons under the metal and plastic devices for scaring away birds.</p>
Full article ">Figure 6
<p>Blocking of the under-roof space apertures: (<b>a</b>), whole bricks cemented in the apertures; (<b>b</b>), plastic bottles full with water stacked in the apertures; (<b>c</b>), part of bricks blocking the apertures; (<b>c</b>), and (<b>d</b>) a pigeon had removed a brick part from the aperture and used the under-roof space for breeding; (<b>e</b>), aperture blocked by nets from outside (green arrow); (<b>f</b>), nets blockade of an aperture from the inside—red arrows indicate the mounting elements.</p>
Full article ">
15 pages, 1735 KiB  
Article
Responses of Sesamum indicum to Allelopathy of Coniferous and Broadleaved Trees
by Yujia Liu, Bingju Zhao, Yumeng Han, Chunjing Zou and Chenghuan Wang
Ecologies 2025, 6(1), 21; https://doi.org/10.3390/ecologies6010021 - 4 Mar 2025
Viewed by 110
Abstract
The relationships among species and the mechanics of those relationships are very complicated in mixed forests, and allelopathy is one of the most important mediators of these relationships. The types and quantities of allelopathic chemicals are different in coniferous and broadleaved trees; studying [...] Read more.
The relationships among species and the mechanics of those relationships are very complicated in mixed forests, and allelopathy is one of the most important mediators of these relationships. The types and quantities of allelopathic chemicals are different in coniferous and broadleaved trees; studying the responses of some sensitive plants, such as certain crops, to allelopathy mediated by the leaf extracts of coniferous and broadleaved trees would be an effective technique to evaluate the relationships among species in a mixed forest. In this paper, the effects of leaf extracts from Metasequoia glyptostroboides, Cedrus deodara, Liquidambar formosana, Platanus acerifolia and a mixture of of coniferous and broadleaved trees on seed germination and seedling growth of Sesamum indicum at a constant concentration (50 gDW/L) were investigated using an indoor filter paper culture dish method. The test results were evaluated using the response index (RI) and the synthesis allelopathic effect index (SE). The results showed that: (1) Four kinds of leaf extracts inhibited the germination and seedling growth of S. indicum. The order of the allelopathic inhibitory effects were as follows: L. formosana > M. glyptostroboides > C. deodara > P. acerifolia; (2) In this experiment, the single leaf extract of the coniferous species (M. glyptostroboides and C. deodara) and the single leaf extract of the broadleaved species (L. formosana and P. acerifolia) did not exhibit significant differences in the direction of the allelopathic effect on S. indicum; (3) Compared to their corresponding single leaf extracts, M. glyptostroboides + P. acerifolia and C. deodara + P. acerifolia mixed leaf extracts promoted the allelopathic effects of S. indicum, namely, the coniferous-broadleaved mixed leaf extract > one single leaf extract > another single leaf extract. The rest of the coniferous-broadleaved mixed leaf extract treatment groups neutralized the allelopathic effects of S. indicum, namely, one single leaf extract > coniferous leaf mixed extract > another single leaf extract. The conclusions could provide a scientific basis for managing forests, especially mixed forest ecosystems. Full article
Show Figures

Figure 1

Figure 1
<p>Effects of leaf extracts from different leaves on the germination process of <span class="html-italic">Sesamum indicum</span>.</p>
Full article ">Figure 2
<p>(<b>A</b>–<b>D</b>) Effects of single leaf extracts and coniferous-broadleaved mixed leaf extracts on the germination process of <span class="html-italic">Sesamum indicum</span>.</p>
Full article ">Figure 2 Cont.
<p>(<b>A</b>–<b>D</b>) Effects of single leaf extracts and coniferous-broadleaved mixed leaf extracts on the germination process of <span class="html-italic">Sesamum indicum</span>.</p>
Full article ">
12 pages, 1282 KiB  
Article
Thermal Requirement for Spring Emergence of Potter Wasp Parancistrocerus fulvipes: Implications for Population Management Under Climate Change
by Roghaiyeh Karimzadeh and Yong-Lak Park
Ecologies 2025, 6(1), 20; https://doi.org/10.3390/ecologies6010020 - 2 Mar 2025
Viewed by 237
Abstract
Parancistrocerus fulvipes (Saussure) (Hymenoptera: Vespidae), a predatory potter wasp, plays a crucial role in ecosystem services by preying on microlepidopteran larvae. This study investigated the effect of the temperature on the spring emergence and survivorship of P. fulvipes. We used seven different [...] Read more.
Parancistrocerus fulvipes (Saussure) (Hymenoptera: Vespidae), a predatory potter wasp, plays a crucial role in ecosystem services by preying on microlepidopteran larvae. This study investigated the effect of the temperature on the spring emergence and survivorship of P. fulvipes. We used seven different temperature regimes ranging from 5 to 38 °C to determine the developmental rate and thermal requirement for the emergence of P. fulvipes at each temperature. The development rates were determined using linear regression and a biophysical model (i.e., the Lactin model). Adult emergence occurred between 22 and 33 °C, and the lower developmental thresholds were 18.5, 17.1, and 17.8 °C for males, females, and both genders combined, respectively. The optimal temperature and upper-temperature threshold for spring emergence were 33 and 38 °C, respectively. The degree-day requirements for adult emergence were 201, 218, and 208 for males, females, and both genders combined. The lowest mortality was observed at 22 °C, while no P. fulvipes emerged at ≤13 °C and ≥38 °C. These findings provide a predictive model for the spring emergence of P. fulvipes, which can optimize ecosystem service programs in various agricultural systems, particularly in the context of climate change and pest management. Full article
(This article belongs to the Special Issue Feature Papers of Ecologies 2024)
Show Figures

Figure 1

Figure 1
<p>Different stages of <span class="html-italic">P. fulvipes</span> in the nest. (<b>a</b>) One egg (yellow arrow) per cell is laid by the female <span class="html-italic">P. fulvipes</span> with provisioned lepidopteran larvae in the cell; (<b>b</b>) a hatched larva (yellow arrow) consumes provisioned prey; (<b>c</b>) a fully grown larva in the overwintering stage; (<b>d</b>,<b>e</b>) the larva becomes a pupa in the spring; (<b>f</b>) the adult <span class="html-italic">P. fulvipes</span> emerges.</p>
Full article ">Figure 2
<p>Nonlinear temperature-dependent development model (Lactin model) of <span class="html-italic">P. fulvipes</span>: (<b>a</b>) males, (<b>b</b>) females, and (<b>c</b>) both genders combined. The open circle indicates a data point that was excluded from the regression analysis because no adult emerged at ≤13 °C.</p>
Full article ">Figure 3
<p>Linear regression of temperature-dependent development of <span class="html-italic">P. fulvipes</span>: (<b>a</b>) males, (<b>b</b>) females, and (<b>c</b>) both genders combined. Only the linear portion of the data was used for regression analyses, and open circles indicate that no adult emerged and thus the data points were excluded from the regression analysis.</p>
Full article ">
15 pages, 2655 KiB  
Article
Environmental Heterogeneity Drives Secondary Metabolite Diversity from Mesquite Pods in Semiarid Regions
by Alfredo Esparza-Orozco, Liliana Carranza-Becerra, Lucía Delgadillo-Ruiz, Juan José Bollaín y Goytia, Norma Angélica Gaytán-Saldaña, Cruz Daniel Mandujano-García, Eladio Delgadillo-Ruiz, Claudia Yared Michel-López, Josefina Huerta-García, Benjamín Valladares-Carranza and Héctor Emmanuel Valtierra-Marín
Ecologies 2025, 6(1), 19; https://doi.org/10.3390/ecologies6010019 - 27 Feb 2025
Viewed by 157
Abstract
Secondary metabolites (SM) in plants play crucial pharmacological, ecological, and nutritional roles for humans, wildlife, and livestock. Environmental Heterogeneity (EH) encompasses the variability of biotic and abiotic factors that influence biological responses of plant species. Advancements in remote sensing have enhanced the ability [...] Read more.
Secondary metabolites (SM) in plants play crucial pharmacological, ecological, and nutritional roles for humans, wildlife, and livestock. Environmental Heterogeneity (EH) encompasses the variability of biotic and abiotic factors that influence biological responses of plant species. Advancements in remote sensing have enhanced the ability to assess plant functional traits more affordably and comprehensively by integrating spectral reflectance data with detailed plant metabolomics. However, studies investigating the relationship between EH—quantified using Rao’s Q heterogeneity index from remote sensing data—and SM diversity remain limited. Here, we present the first report demonstrating that the biotic component of EH, measured as Rao’s Q, is positively associated with SM diversity in mesquite pod extracts—higher Rao’s Q values correspond to greater SM diversity. Generalized additive models (GAMs) revealed that Rao’s Q contributed the most explanatory power, accounting for 21.2% of the deviance, compared to pod weight (13.7%) and pod length (2.03%). However, only the relationship between Rao’s Q and SM diversity was statistically significant (p = 0.029). The Rao’s Q index derived from remote sensing serves as a scalable proxy for identifying SM hotspots, facilitating the targeted discovery of regions with high pharmacological or nutritional value. Full article
Show Figures

Figure 1

Figure 1
<p>Geographic distribution of mesquite trees sampled in three regions. The background shows the 30 × 30 m pixel scale map for land use and vegetation of Zacatecas, Mexico [<a href="#B37-ecologies-06-00019" class="html-bibr">37</a>]. The map was created using the QGIS version 3.28.7 [<a href="#B38-ecologies-06-00019" class="html-bibr">38</a>] software.</p>
Full article ">Figure 2
<p>Boxplot of (<b>a</b>) pod weight and (<b>b</b>) pod size across the southern, central, and northern regions. Each box represents the interquartile range (IQR), spanning from the first quartile (Q1) to the third quartile (Q3). The line inside the box indicates the median (Q2). The whiskers extend to the smallest and largest values within 1.5 × IQR beyond the quartiles.</p>
Full article ">Figure 3
<p>Boxplot showing the number of secondary metabolite classes detected in mesquite pod extracts (SM diversity; y axis) across the southern, central, and northern regions (x axis) using two extraction methods: ultrasound-assisted extraction (UAE) and ethanolic extraction (EE). Each box represents the interquartile range (IQR), spanning from the first quartile (Q1) to the third quartile (Q3). The line inside the box indicates the median (Q2). The whiskers extend to the smallest and largest values within 1.5 × IQR beyond the quartiles.</p>
Full article ">Figure 4
<p>Boxplot of the (<b>a</b>) Soil-Adjusted Vegetation Index (SAVI) and (<b>b</b>) environmental heterogeneity in terms of Rao’s Q observed across the southern, central, and northern regions. Each box represents the interquartile range (IQR), spanning from the first quartile (Q1) to the third quartile (Q3). The line inside the box indicates the median (Q2). The whiskers extend to the smallest and largest values within 1.5 × IQR beyond the quartiles.</p>
Full article ">Figure 5
<p>Principal component analysis (PCA) biplot shows the relationships between explanatory variables (dashed lines)—environmental heterogeneity in terms of Rao’s Q, pod length (cm), and pod weight (g)—and secondary metabolite classes detected (solid lines) in mesquite pods from ultrasound-assisted extraction (UAE), across the southern (gray color), central (blue color), and northern (yellow color) regions. The ellipses represent the three sampled regions based on the abundance of SM classes in each region.</p>
Full article ">Figure 6
<p>Relationships between secondary metabolite diversity (SM diversity; <span class="html-italic">y</span>-axis) and (<b>a</b>) environmental heterogeneity in terms of Rao’s Q, mesquite (<b>b</b>) pod weight and (<b>c</b>) pod size. The black line showed that the generalized additive models fit with the 95% confidence intervals (shaded blue area). The Adjusted coefficient of determination, Adjusted (<span class="html-italic">R</span><sup>2</sup><sub>Adjusted</sub>); probability (<span class="html-italic">p</span>); and Akaike Information Criterion (AIC) are shown.</p>
Full article ">Figure 7
<p>Boxplot showing the secondary metabolite diversity (SM diversity) across the low and high levels of (<b>a</b>) environmental heterogeneity in terms of Rao’s Q, (<b>b</b>) mesquite pod weight, (<b>c</b>) small and large sizes of mesquite pods. Each box represents the interquartile range (IQR), spanning from the first quartile (Q1) to the third quartile (Q3). The line inside the box indicates the median (Q2). The whiskers extend to the smallest and largest values within 1.5 × IQR beyond the quartiles.</p>
Full article ">
16 pages, 1504 KiB  
Article
Population Genetic Structure of Convolvulus persicus L. in the Western Black Sea Region (Romania and Bulgaria) and Its Restricted Distribution
by Elena Monica Mitoi, Carmen Maximilian, Irina Holobiuc, Daniela Mogîldea, Florența-Elena Helepciuc and Claudia Biță-Nicolae
Ecologies 2025, 6(1), 18; https://doi.org/10.3390/ecologies6010018 - 27 Feb 2025
Viewed by 273
Abstract
Convolvulus persicus L. is an endangered narrow-range taxon, characteristic of the habitats along the coastal regions of the Caspian and the Black Seas. The aims of our research were to update the actual distribution area and the genetic evaluation of three representative populations [...] Read more.
Convolvulus persicus L. is an endangered narrow-range taxon, characteristic of the habitats along the coastal regions of the Caspian and the Black Seas. The aims of our research were to update the actual distribution area and the genetic evaluation of three representative populations from the western coastline of the Black Sea located in Sulina, Agigea, and Durankulak. ISSR amplifications were used to assess the genetic intrapopulation diversity and the genetic differentiation among populations. The average genetic polymorphism was 57.8 ± 16.03%. The intrapopulation genetic diversity parameters indicated that the Agigea population exhibits a higher genetic diversity, with this small population being part of the Agigea Marine Dunes Reserve. Although the interpopulation genetic distance was reduced (0.176–0.223) and the distribution of the total variation (AMOVA) was 57% within the population and 43% among the populations, the interpopulation genetic differentiation (PhiPT) was high (0.428, p < 0.001), probably due to the large geographical distances between the remaining populations. The populations’ genetic structures showed a lower genetic distance between the Agigea and Sulina samples. The clonability test supported the vegetative multiplication on the Durankulak and Sulina beaches. Our results showed that the genetic diversity and the distance among the populations in C. persicus were influenced by habitat conditions, destruction, and fragmentation, but also by conservation measures. Full article
(This article belongs to the Special Issue Feature Papers of Ecologies 2024)
Show Figures

Graphical abstract

Graphical abstract
Full article ">Figure 1
<p>Distribution map of <span class="html-italic">C. persicus</span> in area of the Black and Caspian Seas. The numbers represent the distribution sites. The name and coordinates of these sites are listed in <a href="#app1-ecologies-06-00018" class="html-app">Supplementary Materials</a> <a href="#app1-ecologies-06-00018" class="html-app">Table S1</a>.</p>
Full article ">Figure 2
<p>Genetic structure of three <span class="html-italic">C. persicus</span> populations: (<b>a</b>) Neighbor-joining dendrogram and (<b>b</b>) Principal Coordinates Analysis (PCoA) showing the genetic distance between samples (S1–S15 from SP, A1–A15 from AP, D1–D15 from DP).</p>
Full article ">
22 pages, 839 KiB  
Article
Reforestation Initiatives in the Lubumbashi Charcoal Production Basin (DR Congo): Plant Diversity Selection, Management Practices, and Ecosystems Structure
by Dieu-donné N’tambwe Nghonda, Héritier Khoji Muteya, Gracia Kalenga Mupanda, François Duse Dukuku, Nathan Kasanda Mukendi, Bienvenu Esoma Okothomas, Médard Mpanda Mukenza, Sylvestre Cabala Kaleba, François Malaisse, Wilfried Masengo Kalenga, Jan Bogaert and Yannick Useni Sikuzani
Ecologies 2025, 6(1), 17; https://doi.org/10.3390/ecologies6010017 - 14 Feb 2025
Viewed by 396
Abstract
The sustainability of reforestation initiatives depends on the involvement of local communities, whose lack of ownership compromises efforts to combat deforestation in the Lubumbashi Charcoal Production Basin. This study assesses reforestation activities in two village areas (Milando and Mwawa), based on individual interviews [...] Read more.
The sustainability of reforestation initiatives depends on the involvement of local communities, whose lack of ownership compromises efforts to combat deforestation in the Lubumbashi Charcoal Production Basin. This study assesses reforestation activities in two village areas (Milando and Mwawa), based on individual interviews (50 individuals/village area) and floristic inventories carried out in two types of habitats (reforested and unexploited) for each village area. The hypotheses tested were the following: (i) Reforested habitats and tree species were selected collaboratively, ensuring an inclusive approach; (ii) ecological parameters—density per hectare, quadratic mean diameter, basal area, and floristic diversity—of reforested sites were comparable to those of unexploited miombo due to protection allowing natural recovery; and (iii) ethnobotanical and floristic patterns reflect varying levels of anthropogenic disturbance and the limited diversity of species used in reforestation. Thus, the interviews gathered data on habitat and woody species selection for reforestation and management practices, while the inventories assessed the condition of these reforested habitats in terms of density per hectare, basal area, quadratic mean diameter, and floristic diversity. The results show that in both village areas, the selection of habitats for reforestation was carried out concertedly (22.00–44.00% of citations). Woody species were chosen according to the needs of local communities (40–52%) and the availability of seeds (18.00–44.00%). Furthermore, management practices for these reforested habitats include planning/assessment meetings (26.00–38.00%) and maintenance activities, such as firebreaks (38.00–46.00%) and surveillance of reforested habitats (24.00%). Additionally, these practices are being increasingly neglected, jeopardizing reforestation efforts. However, density/ha, basal area, quadratic mean diameter, and floristic diversity did not show significant differences between reforested and unexploited habitats, particularly at Milando (p > 0.05). Furthermore, floristic similarity is 55.56% for reforested habitats and 93.75% for unexploited habitats but remains low between reforested and unexploited habitats (40.00–47.62%). This similarity between ethnobotanical and floristic lists is also low (43.75–31.58%). Finally, a total of 442 woody individuals were recorded in reforested habitats and 630 in unexploited ones, with Fabaceae dominating both habitat types. Despite some cited reforestation species like Acacia polyacantha being absent, Brachystegia spiciformis emerged as the most prevalent species in both reforested and unexploited areas. The results of the present study suggest a sustainable and continuous management of these reforested habitats for an effective reconstitution of the forest cover. To reinforce the sustainable management of these reforested habitats, it is recommended that decision-makers conduct awareness-raising campaigns and establish payment for environmental service mechanisms to motivate communities. Full article
Show Figures

Figure 1

Figure 1
<p>Location of the city of Lubumbashi (gray polygon) and its rural area (white space around the city of Lubumbashi). The triangles represent the village areas covered by the present study. The geographic coordinates used to locate these two village areas were taken from reforested habitats using GPS.</p>
Full article ">Figure 2
<p>Diametric structure of habitats in both village areas: (<b>a</b>): reforested habitats; (<b>b</b>): unexploited habitats.</p>
Full article ">
66 pages, 27848 KiB  
Article
Climate Change Influences on Central European Insect Fauna over the Last 50 Years: Mediterranean Influx and Non-Native Species
by Attila Haris, Zsolt Józan, Péter Schmidt, Gábor Glemba, Bogdan Tomozii, György Csóka, Anikó Hirka, Peter Šima and Sándor Tóth
Ecologies 2025, 6(1), 16; https://doi.org/10.3390/ecologies6010016 - 13 Feb 2025
Viewed by 1837
Abstract
The Central European fauna, in the last decades, has been undergoing a strong transformation due to four main factors: the retreat of living organisms that require cool and wet habitats, the proliferation of organisms that thrive in warm and dry conditions, the northward [...] Read more.
The Central European fauna, in the last decades, has been undergoing a strong transformation due to four main factors: the retreat of living organisms that require cool and wet habitats, the proliferation of organisms that thrive in warm and dry conditions, the northward migration of Mediterranean organisms, and the gradual establishment of plants and animals with tropical origins. In this study, we detail the changes in the orders Diptera, Hymenoptera, and Lepidoptera and analyze the establishment of non native insects and the northward migration of Mediterranean insect species. The transformation towards a Mediterranean-type fauna is prominently indicated by the population in total abundance increase of xerothermic Aculeata, bee flies (Bombyliidae), and horse flies (Tabanidae). Additionally, groups that require cool and wet ecological conditions, particularly hoverflies (Syrphidae), but also sawflies (Tenthredinidae) and tachinid flies (Tachinidae), have shown a notable decline. In nocturnal moths, we observe a decrease in species richness in certain areas, as well as frequent outbreaks in populations of some less climate-sensitive species. Some species of butterflies are less sensitive to the current extent of climate change, exhibiting significant population in total abundance growth under protected conditions. However, most of the previously sporadic and rare butterfly species have proven to be climate-sensitive, unable to achieve significant population in abundance growth even under strict nature conservation. In recent decades, the influx from Mediterranean regions and the establishment of tropical non native insect species have turned at an exponential rate. We have reviewed the presence of alien insect species, recording 803 alien insect species in our region; 298 of them have arrived in the past quarter-century, with a significant proportion (54%) originating from tropical and Mediterranean regions. Full article
(This article belongs to the Special Issue Feature Papers of Ecologies 2024)
Show Figures

Figure 1

Figure 1
<p>The <span class="html-italic">Graphocephala fennahi</span> Young, 1977 (Rhododendron Leafhopper), native to North America, were first found on the leaves of Rhododendron catawbiense in Hungary in 2012. It well illustrates the role of alien insect species in the transformation of our fauna (photo: György Csóka).</p>
Full article ">Figure 2
<p>Biogeographic map of the investigated area. Pannonian (brown), Continental (green), and Alpine biogeographic regions (violet). (source: EEA [<a href="#B7-ecologies-06-00016" class="html-bibr">7</a>]).</p>
Full article ">Figure 3
<p>Hydrogeological map of the Carpathian Basin (source: [<a href="#B8-ecologies-06-00016" class="html-bibr">8</a>]).</p>
Full article ">Figure 4
<p>Average annual temperatures of three Central European countries between 1970 and 2023. Green: Hungary, orange: Romania, red: Slovakia. Climatic data from World Bank Portal [<a href="#B19-ecologies-06-00016" class="html-bibr">19</a>].</p>
Full article ">Figure 5
<p>Long-term trend of horse-flies (Tabanidae) in the Carpathian Basin.</p>
Full article ">Figure 6
<p>Long-term declining trend of hoverflies (Syrphidae) in the Carpathian Basin.</p>
Full article ">Figure 7
<p>Long-term increasing trend of xerotherm bee flies (Bombyliidae) in the Carpathian Basin, winners of the warming climatic conditions.</p>
Full article ">Figure 8
<p>Long-term trend of tachinid flies (Tachinidae) in the Carpathian Basin. General declining trend with strong fluctuation probably typical for parasitoids.</p>
Full article ">Figure 9
<p>Long-term trend of species richness of Bumblebees in the high (blue) and low (red) elevations of the Carpathian Basin.</p>
Full article ">Figure 10
<p>Long-term trend of wild bee families in the Carpathian Basin.</p>
Full article ">Figure 11
<p>Long-term trend of Bembecidae, Psenidae, Sphecidae and Pemphedronidae in the Carpathian Basint.</p>
Full article ">Figure 12
<p>Long-term trend of Chrysididae, Philantidae and Crabronidae in the Carpathian Basin.</p>
Full article ">Figure 13
<p>Long-term trend of numbers of specimens of sawflies (Symphyta) by Malaise trap method based on Haris et al., 2024 [<a href="#B6-ecologies-06-00016" class="html-bibr">6</a>]. Sawflies are primarily distributed in northern and montane regions, mostly inhabiting moderately cool, rainy areas.</p>
Full article ">Figure 14
<p>Long-term trend of species richness of sawflies (Symphyta) by Malaise trap method based on Haris et al., 2024 [<a href="#B6-ecologies-06-00016" class="html-bibr">6</a>].</p>
Full article ">Figure 15
<p><span class="html-italic">Aglais urticae</span> (Linnaeus, 1758) (Small Tortoiseshell) was once common until the late 1980s. In the last decades, it nearly disappeared from the deeper region of the Carpathian Basin (photo: Ádám Gór).</p>
Full article ">Figure 16
<p><span class="html-italic">Brintesia circe</span> (Fabricius, 1775) (Great Banded Grayling) has successfully resisted climate change so far (photo: Péter Schmidt).</p>
Full article ">Figure 17
<p>Some butterflies, like <span class="html-italic">Iphiclides podalirius</span> (Linnaeus, 1758) (Scarce Swallowtail), have even been able to increase their abundance in Central Europe (Photo: Gábor Glemba).</p>
Full article ">Figure 18
<p>Changes in nocturnal macrolepidoptera populations in total abundance between 1970 and 2022.</p>
Full article ">Figure 19
<p>Changes in nocturnal macrolepidoptera populations in total abundance between 2014 and 2022.</p>
Full article ">Figure 20
<p>Changes in species richness of nocturnal macrolepidoptera between 1970 and 2022.</p>
Full article ">Figure 21
<p>Timeline of non-native insects in the Carpathian Basin from the Neolithic period till 2024.</p>
Full article ">Figure 22
<p>Timeline of the introduction of tropical insect species.</p>
Full article ">Figure 23
<p>Division of non-native insects according to their taxonomic groups.</p>
Full article ">Figure 24
<p>Division of non-native insects according to their origin.</p>
Full article ">Figure 25
<p><span class="html-italic">Ovalisia festiva</span> (Linnaeus, 1767) (Cypress Jewel Beetle) had double colonization: natural and introduction with ornamental plants (photo: György Csóka).</p>
Full article ">Figure 26
<p>Timeline of the influx of Mediterranean insect species.</p>
Full article ">Figure 27
<p>Long-term trend of wild bees in Belgium’s aboundances (after Duchenne et al. [<a href="#B202-ecologies-06-00016" class="html-bibr">202</a>]).</p>
Full article ">Figure 28
<p>The <span class="html-italic">Parnassius mnemosyne</span> (Linnaeus, 1758) (Clouded Apollo) appears stable in our region (photo: Gábor Glemba).</p>
Full article ">Figure 29
<p>Different types of increase of insect populations in abundance as a response to climate change (yellow: exponential growth of invasive insect, red: moderate population growth after the temperature optimum, blue: continuous growth of abundance of xerotherm insect).</p>
Full article ">Figure 30
<p>Different types of decline of insect abundances as a response to climate change (yellow: exponential decline of highly sensitive insects of climate change, red: gradual decline of population in abundance of hylophilous insects, blue: disappearance of climate change-sensitive butterfly species).</p>
Full article ">
21 pages, 2023 KiB  
Article
Klina River Water Quality Assessment Based on Diatom Algae
by Osman Fetoshi, Romina Koto, Albona Shala, Fatbardh Sallaku, Pajtim Bytyçi, Demokrat Nuha, Bojan Đurin, Rozeta Hasalliu, Arbëri Bytyçi, Upaka Rathnayake and Dragana Dogančić
Ecologies 2025, 6(1), 15; https://doi.org/10.3390/ecologies6010015 - 8 Feb 2025
Viewed by 692
Abstract
Benthic diatoms are being used as indicators to assess the biological quality of surface waters in Kosovo. The Klina River is the left tributary of the White Drin River Basin, with a length of 69 km. The study assessed the level of surface [...] Read more.
Benthic diatoms are being used as indicators to assess the biological quality of surface waters in Kosovo. The Klina River is the left tributary of the White Drin River Basin, with a length of 69 km. The study assessed the level of surface water quality in the Klina River using 12 diatomic indices calculated with the Omnidia program. For this purpose, three stations monitored the river Klina in the autumn of 2021 to conform to international standards. A total of 88 diatom taxa were identified, with the dominant species being Rhoicosphenia abbreviata (C. Agardh) Lange-Bertalot, Gyrosigma acuminatum (Kützing) Rabenhorst, Cocconeis placenula Ehrenberg, Gomphonema minutum (Ag.) Agardh f. minutum, Gomphonema clavatum Ehr, Meridion circulare (Greville) C.A. Agardh, Cocconeis pediculus Ehrenberg, Diatoma vulgaris Bory, and Nitzschia dissipata (Kützing) Grunow ssp. dissipata etc. This study assessed the surface water quality in the Klina River using diatom indices, indicating that the river is in good to moderate ecological condition. Environmental variables such as hydrogen ion concentration (pH) and dissolved oxygen (DO) had significant positive correlations (<0.01) with the biological diatom index (IBD), Descy’s pollution metric (Descy), Sladeček’s pollution metric (SLA), the European index (CEE), and Watanabe’s Index (WAT), while the total suspended solids (TSS) also showed a strong negative significant correlation (<0.01) with the generic diatom index (IDG), Indice Diatomique Artois Picardie (IDAP), the eutrophication pollution index (EPI-D), the trophic diatom index (TDI), the Pampean diatom index (IDP), and Steinberg and Schiefele’s index (SHE). Total phosphorus (TP), biochemical oxygen demand (BOD), and chemical oxygen demand (COD) presented a significant negative correlation (<0.05) with the IBD, Descy, SLA, CEE, and WAT indices. Our findings provide insights for organizations dealing with the state of the environment and water protection in Kosovo, and these results can be used as a starting point for assessing the ecological quality of water and monitoring environmental pollution in the Kosovo region. Full article
Show Figures

Figure 1

Figure 1
<p>Sampling locations and investigation areas.</p>
Full article ">Figure 2
<p>The methodology of determination of diatom.</p>
Full article ">Figure 3
<p>Results of physicochemical analysis in Klina River.</p>
Full article ">Figure 4
<p>Ordination plot of principal components analysis (PCA) of physicochemical parameters.</p>
Full article ">Figure 5
<p>Canonical correspondence analysis (CCA) diagram showing environmental variables and the species of diatoms that were the most abundant.</p>
Full article ">
19 pages, 5477 KiB  
Article
Quantifying the Water Sources of Riparian Plants for Different Life-Forms and Water Ecotypes in the Yongding River Basin
by Liangsuo Ren and Mingjie Luo
Ecologies 2025, 6(1), 14; https://doi.org/10.3390/ecologies6010014 - 5 Feb 2025
Viewed by 382
Abstract
Riparian zones, acting as transitional areas between aquatic and terrestrial ecosystems, boast a rich diversity of plant species. However, alterations in river hydrological regimes can significantly impact plant growth and distribution. In this study, seven typical reaches of Yongding River Basin were selected, [...] Read more.
Riparian zones, acting as transitional areas between aquatic and terrestrial ecosystems, boast a rich diversity of plant species. However, alterations in river hydrological regimes can significantly impact plant growth and distribution. In this study, seven typical reaches of Yongding River Basin were selected, and xylem water, soil water at different depths, and river water were collected in May and August. By measuring δ2H and δ18O values and combining with MixSIAR model, the proportion of water utilization by plants from different sources was quantified. The findings revealed that δ2H and δ18O values of river water, soil water, and plant xylem water were higher in August compared to May. While there was no significant difference in δ2H and δ18O values between river and soil water during different periods (p > 0.05), significant differences were observed in δ18O in plant xylem water (p = 0.022). Regardless of whether it was May or August, herbaceous plants utilized river water more extensively than trees and shrubs, and hydrophytes exhibited a higher dependence on river water compared to mesophytes and xerophytes. Some hygrophytes (P. anserina, etc.) utilized river water for over 90% of their total water intake. There were significant differences between herbs and trees and shrubs in the proportion of river water usage in August (p = 0.001). Moreover, considerable variations existed in the proportion of river water usage among different water ecotypes in both May (p = 0.005) and August (p < 0.001). Our findings provide a scientific basis for the rational allocation of plants in the process of riparian vegetation restoration. Full article
Show Figures

Figure 1

Figure 1
<p>Geographical location of the study area (S1–S7 show photographs of the riparian zone in the selected seven reaches).</p>
Full article ">Figure 2
<p>The plots of δ<sup>2</sup>H and δ<sup>18</sup>O values in river, soil, and plant xylem water at the sites (GMWL: Global Meteoric Water Line, LMWL: Local Meteoric Water Line).</p>
Full article ">Figure 3
<p>Water use proportion of trees, shrubs, and dominant herbaceous plants in the riparian zone based on the MixSIAR model (M: May; A: August).</p>
Full article ">Figure 3 Cont.
<p>Water use proportion of trees, shrubs, and dominant herbaceous plants in the riparian zone based on the MixSIAR model (M: May; A: August).</p>
Full article ">Figure 3 Cont.
<p>Water use proportion of trees, shrubs, and dominant herbaceous plants in the riparian zone based on the MixSIAR model (M: May; A: August).</p>
Full article ">Figure 3 Cont.
<p>Water use proportion of trees, shrubs, and dominant herbaceous plants in the riparian zone based on the MixSIAR model (M: May; A: August).</p>
Full article ">Figure 4
<p>The distribution of water use proportions for herbaceous plants.</p>
Full article ">Figure 5
<p>The distribution of water use proportions for trees and shrubs.</p>
Full article ">Figure 6
<p>The distribution of water use proportions for hydrophytes.</p>
Full article ">Figure 7
<p>The distribution of water use proportions for mesophytes.</p>
Full article ">Figure 8
<p>The distribution of water use proportions for xerophytes.</p>
Full article ">Figure 9
<p>The distribution characteristics of hydrogen and oxygen isotope values in Yongding River Basin.</p>
Full article ">
21 pages, 3159 KiB  
Article
Recovery of Streams in the Harz National Park (Germany)—The Attenuation of Acidification
by Uta Langheinrich, Kilian E. C. Smith, Jose Ramon Arevalo, Fabian Schwarz and Volker Lüderitz
Ecologies 2025, 6(1), 13; https://doi.org/10.3390/ecologies6010013 - 2 Feb 2025
Viewed by 738
Abstract
Between 1995 and 2022, 19 measuring points in small and medium sized streams in the Harz National Park, Germany, were sampled. The samples were evaluated in terms of their macroinvertebrate (MI) biology and hydrochemistry. Nearly all streams showed a natural hydromorphology, and low [...] Read more.
Between 1995 and 2022, 19 measuring points in small and medium sized streams in the Harz National Park, Germany, were sampled. The samples were evaluated in terms of their macroinvertebrate (MI) biology and hydrochemistry. Nearly all streams showed a natural hydromorphology, and low values of biological oxygen demand (BOD) characteristic for rivers not contaminated by organic matter. Nevertheless, in the 1990s, most streams were still only settled by a small number of MI species. However, by 2022, the MI species number had doubled or tripled in most cases, with a maximum increase from 14 to 52. There is a clear correlation between species number and pH. At 15 of the 19 sampling sites, the acidity class has gotten better by at least one value. Thus, acid-sensitive species, mainly from the taxonomic orders Trichoptera, Plecoptera, and Ephemeroptera, have been able to settle higher altitudes, as well as formerly acidic reaches. In general, the streams contain a very specific macroinvertebrate fauna that emphasizes the conservation value of the Harz National Park. Attenuation of acidification has not only influenced the MI diversity. Along with the increase in pH, fish populations have recovered, and formerly fish-free stream sections have been recolonised. The biological recovery of the streams has also been fostered by the breakdown of spruce forest monocultures in the surroundings, the natural development of deciduous trees on the banks, and increasing levels of DOC (dissolved organic carbon). Full article
Show Figures

Figure 1

Figure 1
<p>Location of the National Park and the adjacent towns and villages. The yellow, red, and green circle is the official symbol of Harz National Park. (Picture: Mandy Gebara, National Park Harz).</p>
Full article ">Figure 2
<p>Photos showing the changes in shading for selected sampling sites due to forest dieback. The locations and details of the sampling sites are given below. (Pictures: Uta Langheinrich).</p>
Full article ">Figure 3
<p>Map showing the locations of the 19 sampling sites on different streams (Source: Q-GIS Version 3.34.1, changed).</p>
Full article ">Figure 4
<p>Correlations between (<b>A</b>) temperature and pH and (<b>B</b>) pH and dissolved aluminium (Al<sup>3+</sup>, mg/L) for Site 5 on the Ilse River.</p>
Full article ">Figure 5
<p>Relationship between species richness of MIs and pH.</p>
Full article ">Figure 6
<p><b>Top</b>: Development of species numbers (<b>left</b>) and pH mean (<b>right</b>) for 11 sampling sites (1–11) that were sampled between 1994 and 1996 and again in 2022. <b>Bottom</b>: Development of species numbers (<b>left</b>) and pH mean (<b>right</b>) for sampling sites 14–19 that were sampled between 2008 and 2010 and again in 2022. (◦ outlier).</p>
Full article ">Figure 7
<p>Stream sample site scores in the space defined by axes I and II of the Detrended Correspondence Analysis (DCA) based on the matrix density of the species. Acidified sites are on the right side and neutral ones on the left (sites with pH over 7 are indicated in blue, while sites with pH below 6 are indicated in orange). The first number is the site, while the second number (followed by the underscore) is the sampling year, the first sampling year in case this took place over several years (see <a href="#ecologies-06-00013-t004" class="html-table">Table 4</a>).</p>
Full article ">
12 pages, 1323 KiB  
Article
Species-Specific Effects of a Sound Prototype to Reduce Bird Use of Powerline Poles
by Joana Ribeiro-Silva, Hélder Ribeiro, Nuno M. Pedroso, António Mira and Neftalí Sillero
Ecologies 2025, 6(1), 12; https://doi.org/10.3390/ecologies6010012 - 2 Feb 2025
Viewed by 540
Abstract
Powerlines pose a significant threat to many bird species, impacting their conservation. Current research focuses on developing methods to mitigate bird mortality due to electrocution and collisions with powerlines. In this study, we designed a sound prototype to be installed on infrastructure poles, [...] Read more.
Powerlines pose a significant threat to many bird species, impacting their conservation. Current research focuses on developing methods to mitigate bird mortality due to electrocution and collisions with powerlines. In this study, we designed a sound prototype to be installed on infrastructure poles, including powerlines, aiming to reduce their use by birds. We conducted bird surveys over 47 days, from February to May 2020, in five light poles: the central pole where the device was installed (0 m), two poles at 25 m, and two poles at 50 m from the central pole. The first 10 days served as a control period with the deterrent device switched off, followed by 37 days with the device switched on. In total, we recorded 1945 bird observations, of which 1569 occurred with the device on. The device was triggered by bird movements, resulting in 588 reactions to sound. When activated, 10.6% of large- and medium-sized birds were flushed from the surveyed poles: 2.6% were already perched and flushed due to the sound, 3.9% were prevented from perching, and 4.1% were flushed after perching, thereby reducing the risk of electrocution. Among the birds perching or approaching the pole where the device was installed, 25% were deterred by the sound. The black kite, Milvus migrans, was the most reactive species to the device (54.3% flushed at 0 m, and 8.8% flushed at 25 and 50 m), while the white stork, Ciconia ciconia, showed the least sensitivity to the disturbances (14.4% flushed at 0 m, and 2.7% flushed at 25 and 50 m). The corvids exhibited a response rate between the other two species (33.3% flushed at 0 m, and 6.8% flushed at 25 and 50 m). We identified significant limitations to this prototype and proposed recommendations to improve its efficiency. Full article
Show Figures

Figure 1

Figure 1
<p>Deterrent device with the location of the PIR sensors (indicated by arrows).</p>
Full article ">Figure 2
<p>(<b>A</b>) Proportion (%) of white storks, corvids, and black kites perching and approaching the poles with the deterrent device (prototype) switched off and with the device switched on (8 periods). (<b>B</b>) Proportion (%) of individuals (all species pooled) that flushed and did not flush in response to the sound of the device according to the distance of the light pole to the deterrent device (0, 25, 50 m). (<b>C</b>) Proportion (%) of white storks, corvids, and black kites that flushed and did not flush on the central pole (0 m) in response to the sound of the device. (<b>D</b>) Proportion (%) of white storks, corvids, and black kites that flushed and did not flush on the farthest poles (25 and 50 m) in response to the sound of the device. (<b>E</b>) Proportion (%) of white storks, corvids, and black kites that did not perch, perched and flushed afterwards, and landed and stayed perched at the poles while the sound was active.</p>
Full article ">Figure 3
<p>Mean (±S.E.) number of (<b>A</b>) white storks, (<b>B</b>) corvids, and (<b>C</b>) black kites recorded perching or approaching the poles at the distances of 0, 25, 50 m from the deterrent device, during the different periods.</p>
Full article ">Figure 4
<p>Mean (±S.E.) number of (<b>A</b>) white storks, (<b>B</b>) corvids, and (<b>C</b>) black kites that flushed and did not flush in response to the device sound on the poles 0, 25, 50 m from the deterrent device, during the different periods when the device was switched on.</p>
Full article ">
17 pages, 4713 KiB  
Article
Rapoport’s Rule, the Ecotone Concept, and Salinity Gradient Predict the Distribution of Benthic Foraminifera in a Southeastern Pacific Estuary
by Leonardo D. Fernández and Margarita Marchant
Ecologies 2025, 6(1), 11; https://doi.org/10.3390/ecologies6010011 - 2 Feb 2025
Viewed by 465
Abstract
This study explores the biogeographic processes shaping the distribution of benthic foraminifera along a salinity gradient in the Contaco Estuary, southeastern Pacific, Chile. The primary aim was to evaluate the applicability of key ecological paradigms—Rapoport’s rule, the mid-domain effect, ecotones, and source–sink dynamics—to [...] Read more.
This study explores the biogeographic processes shaping the distribution of benthic foraminifera along a salinity gradient in the Contaco Estuary, southeastern Pacific, Chile. The primary aim was to evaluate the applicability of key ecological paradigms—Rapoport’s rule, the mid-domain effect, ecotones, and source–sink dynamics—to unicellular eukaryotes in estuarine environments. A 1550 m longitudinal transect, sampled at 50 m intervals, revealed a pronounced salinity-driven pattern in species richness and diversity, with calcareous taxa dominating euhaline zones and agglutinated taxa thriving in brackish and freshwater areas. Source–sink dynamics were not supported, as beta diversity analyses identified turnover as the dominant driver, highlighting species replacement along the salinity gradient. Evidence of a longitudinal Rapoport effect was observed, with broader distribution ranges in low-salinity environments, reflecting adaptations to suboptimal conditions. Contrary to predictions, the mid-domain effect was not supported, as foraminiferal richness showed a monotonic decline. These findings extend macroecological principles to microbial communities, emphasizing deterministic processes in shaping estuarine diversity. This research provides a robust framework for understanding biodiversity patterns in dynamic ecosystems, offering valuable insights for conservation and ecological monitoring. Full article
Show Figures

Figure 1

Figure 1
<p>Location of the Contaco Estuary on the southeastern Pacific coast of Chile. The left panel highlights the position of the estuary in Chile (green triangle) within South America. The central panel shows a high-resolution satellite view of the estuary, sampling sites and its surrounding area, including the rural village of Pucatrihue. The right panel shows depth variation across sampling sites in the Contaco Estuary. The y-axis represents the sampling sites ordered sequentially from the estuary mouth (site 1) to the head (site 32), while the x-axis indicates water depth (m) at each site. Red dots represent measured depth values, and the dashed line connects sequential sites to illustrate depth fluctuations along the estuarine gradient. Map data © OpenStreetMap contributors and MapTiler.</p>
Full article ">Figure 2
<p>Salinity recorded along the Contaco Estuary. As expected, salinity values (black dots) decrease significantly from the mouth to the head of the estuary (black dashed line, <span class="html-italic">r</span><sup>2</sup> = 0.382, <span class="html-italic">p</span> &lt; 0.0001). Three water types were identified in the Contaco Estuary based on salinity levels: euhaline (30–40 psu), brackish (0.5–29 psu), and freshwater (&lt;0.5 psu).</p>
Full article ">Figure 3
<p>Species richness (number of species) and diversity (Shannon–Wiener diversity index) along the Contaco Estuary salinity gradient. (<b>a</b>) Species richness ranged from 24 to 2 species, while diversity ranged from 1.8 to 0.6. Both metrics showed a monotonic decrease from the estuary mouth to its head along with the observed salinity gradient. (<b>b</b>) Richness and diversity exhibited strong positive correlations with salinity: richness (<span class="html-italic">r</span><sup>2</sup> = 0.823, <span class="html-italic">p</span> &lt; 0.0001) and diversity (<span class="html-italic">r</span><sup>2</sup> = 0.553, <span class="html-italic">p</span> &lt; 0.0001). Panel (<b>a</b>) displays actual salinity values measured at ~50 m intervals along the estuary from mouth to head, while panel (<b>b</b>) illustrates the relationship between diversity metrics and log-transformed salinity values. These results highlight the influence of salinity on community composition and diversity patterns in the estuary.</p>
Full article ">Figure 4
<p>Spatial patterns and relationships between total, calcareous, and agglutinated foraminiferal abundance and salinity in the Contaco Estuary. (<b>a</b>) Total abundance, along with calcareous and agglutinated species, plotted against observed salinity (psu) measured from the estuary mouth to its head. The data reflect distinct tolerance levels, with calcareous species peaking in euhaline waters and agglutinated species in brackish waters. Notice the overlap between total abundance (red points) and calcareous species abundance (yellow points), resulting in orange points at the mouth of the estuary. (<b>b</b>) Relationship between total abundance and log-transformed salinity (log<sub>10</sub>[psu]), showing a positive correlation (<span class="html-italic">r</span><sup>2</sup> = 0.239, <span class="html-italic">p</span> &lt; 0.001). (<b>c</b>) Abundance of calcareous and agglutinated species plotted against log-transformed salinity. Both groups show significant positive correlations with salinity: calcareous species (<span class="html-italic">r</span><sup>2</sup> = 0.756, <span class="html-italic">p</span> &lt; 0.0001) and agglutinated species (<span class="html-italic">r</span><sup>2</sup> = 0.551, <span class="html-italic">p</span> &lt; 0.0001).</p>
Full article ">Figure 5
<p>Relationships between the abundance of dominant foraminiferal species and salinity across the Contaco Estuary. (<b>a</b>) Scanning electron microscopy (SEM) images of the four dominant taxa, which account for 87% of the total abundance in the Contaco Estuary. Top row, from left to right: <span class="html-italic">Ammonia</span> spp. (calcareous) and <span class="html-italic">Haplophragmoides wilberti</span> (agglutinated). Bottom row, from left to right: <span class="html-italic">Miliammina fusca</span> (agglutinated) and <span class="html-italic">Trochamminita salsa</span> (agglutinated). (<b>b</b>) Longitudinal abundance patterns of the four dominant species along the observed salinity gradient, ranging from the estuary mouth (euhaline waters) to its head (freshwater). Each species shows a clear decrease in abundance upstream as salinity declines. Salinity values (psu) are plotted in their natural sequence, from highest to lowest, reflecting their actual longitudinal distribution along the estuarine gradient. The data highlight distinct salinity tolerance levels among taxa. (<b>c</b>) Abundance of the four dominant taxa as a function of log-transformed salinity (log<sub>10</sub>[psu]), with dashed lines representing regression fits for each taxon (<span class="html-italic">Ammonia</span> spp., <span class="html-italic">r</span><sup>2</sup> = 0.779, <span class="html-italic">p</span> &lt; 0.0001; <span class="html-italic">M. fusca</span>, <span class="html-italic">r</span><sup>2</sup> = 0.439, <span class="html-italic">p</span> &lt; 0.0001; <span class="html-italic">H. wilberti</span>, <span class="html-italic">r</span><sup>2</sup> = 0.234, <span class="html-italic">p</span> &lt; 0.0001; <span class="html-italic">T. salsa</span>, <span class="html-italic">r</span><sup>2</sup> = 0.472, <span class="html-italic">p</span> &lt; 0.0001).</p>
Full article ">Figure 6
<p>Rarefaction and extrapolation curves estimated using abundance data of foraminifera from the Contaco Estuary. To facilitate visualization, only the curves for the first five sampling sites (0, 50, 100, 150, and 200 m from the estuary mouth) are shown. Full rarefaction and extrapolation curves, including confidence intervals for all 32 sites, are available in <a href="#app1-ecologies-06-00011" class="html-app">Figure S1</a>. Solid lines represent rarefaction, while dashed lines indicate extrapolation. Circles along the curves denote the observed species richness based on the total number of individuals collected at each site. The x-axis reflects the number of individuals per 10 cm<sup>3</sup>, and the y-axis indicates species richness. These results demonstrate effective sampling coverage, with most sites approaching an asymptote in species richness before extrapolation.</p>
Full article ">Figure 7
<p>(<b>a</b>) Rapoport’s rule: a significant positive relationship between range extent and range midpoint for the 31 species recorded (<span class="html-italic">r</span><sup>2</sup> = 0.645, <span class="html-italic">p</span> &lt; 0.0001) supports the existence of Rapoport’s longitudinal rule in the Contaco Estuary. The number of visible data points is smaller than the actual number due to overlapping values, i.e., darker red points represent higher overlap density. (<b>b</b>) Mid-domain effect: observed species richness (red circles) as a function of distance from the estuary mouth compared to the richness predicted by the upper and lower 95% confidence intervals of the mid-domain effect null model (green dashed lines). The empirical richness pattern diverged from the hump-shaped richness pattern predicted by the null model.</p>
Full article ">Figure 8
<p>Summary of beta diversity components, clustering, NMDS, and species richness modeling results for benthic foraminiferal communities in the Contaco Estuary. (<b>a</b>) Beta diversity (β<sub>SOR</sub> = 0.921) is primarily driven by turnover (β<sub>SIM</sub> = 0.743) rather than nestedness (β<sub>SNE</sub> = 0.178), indicating that species replacement underlies the spatial variation in community composition among sampling sites (i.e., beta diversity). (<b>b</b>) A Bray–Curtis clustering analysis identified two distinct groups of sampling sites, aligning with the results of the NMDS. (<b>c</b>) Non-metric multidimensional scaling (NMDS) ordination confirms the presence of two discrete communities, as highlighted by 95% confidence ellipses. (<b>d</b>) Species richness modeling in PAST shows a peak of observed richness significantly higher than the null model prediction at the estuary’s mouth. This peak likely represents a transitional zone where calcareous and agglutinated species co-occur, forming a central community predicted by the TA-pattern. However, the narrow spatial extent of this ecotone may render it undetectable in clustering and ordination analyses. Together, these findings suggest the presence of two main communities rather than the three predicted by the TA-pattern.</p>
Full article ">
16 pages, 5114 KiB  
Article
Towed Video-Diver: A Useful Low-Cost Tool for Rapid Benthic Mapping and Biodiversity Monitoring
by Gonzalo Bravo, Gaston A. Trobbiani, Gregorio Bigatti, Lucas E. Beltramino and Alejo J. Irigoyen
Ecologies 2025, 6(1), 10; https://doi.org/10.3390/ecologies6010010 - 2 Feb 2025
Viewed by 563
Abstract
Marine Protected Areas (MPAs) require efficient monitoring tools to assess habitats and biodiversity, particularly in remote or understudied regions. This study demonstrates the utility of the towed video-diver technique combined with high-resolution video for rapidly surveying benthic habitats and associated taxa. Applied in [...] Read more.
Marine Protected Areas (MPAs) require efficient monitoring tools to assess habitats and biodiversity, particularly in remote or understudied regions. This study demonstrates the utility of the towed video-diver technique combined with high-resolution video for rapidly surveying benthic habitats and associated taxa. Applied in Arredondo, a shallow bay within an MPA in Atlantic Patagonia, the method covered 14,000 m2 through eight transects, utilizing just 180 min of dive time and ~300 min of video analysis. Substrate types and their associated taxa were classified using the CATAMI framework, yielding a list of 28 taxa and density estimates of mobile organisms. Additionally, the percentage cover of Gracilaria sp.—a commercially valuable macroalga historically overexploited in the region—was estimated for the bay. The invasive crab Carcinus maenas was found across all substrate types on the bay, underscoring its ecological tolerance and the need for ongoing monitoring. This cost-effective, rapid methodology is highly effective for detecting and describing areas of ecological or conservation interest, providing critical baseline data for targeted, detailed studies. Its simplicity and efficiency make it ideal for initial surveys in remote regions, supporting the conservation and management of MPAs. Full article
Show Figures

Figure 1

Figure 1
<p>Location of Arredondo Bay in the national park PIMCPA. The park boundaries are shown as dashed lines in the upper panel, and the GPS tow boat track is represented by yellow lines in the lower panel.</p>
Full article ">Figure 2
<p>Diagram of the sampling TVD system, where the diver is towed by a small vessel (towboat). Illustration by Candelaria Belén Piemonte.</p>
Full article ">Figure 3
<p>Maps of bottom types. (<b>A</b>): Bottom type map generated using linear interpolation with all substrate types combined. (<b>B</b>): Bottom type map with separately interpolating soft and hard substrates, which are then overlaid. This map also includes the presence of ripples observed on the soft substrates.</p>
Full article ">Figure 4
<p>Maps of bottom types overlaid with the presence of various taxa, including crabs (<b>A</b>–<b>D</b>), fish (<b>E</b>), the gastropod <span class="html-italic">Odontocymbiola magellanica</span> (<b>F</b>), the anemone Antholoba achates epibiont of <span class="html-italic">Adelomelon ancilla</span> (<b>G</b>), <span class="html-italic">Metridium</span> sp. (<b>H</b>), sea stars (<b>I</b>), the tunicate <span class="html-italic">Polyzoa opuntia</span> (<b>J</b>), the giant algae <span class="html-italic">Macrocystis pyrifera</span> (<b>K</b>), and coverage of the macroalgae <span class="html-italic">Gracilaria</span> sp. (<b>L</b>). Taxa illustrations by Candelaria Belén Piemonte.</p>
Full article ">
21 pages, 2757 KiB  
Article
Analysis of the Protocols for Action Against Strandings of Sea Turtles and Their Evolution in Rehabilitation on Tenerife Island (Canary Islands, Spain)
by Beatriz López Vega, Claudia Hurtado-Pampín and Raquel de la Cruz-Modino
Ecologies 2025, 6(1), 9; https://doi.org/10.3390/ecologies6010009 - 24 Jan 2025
Viewed by 638
Abstract
Numerous interactions between human activities and wildlife currently impact various species. In recent decades, these activities have contributed to declining sea turtle populations. The waters around Spain serve as important staging areas for sea turtles, particularly Caretta caretta, which spend part of [...] Read more.
Numerous interactions between human activities and wildlife currently impact various species. In recent decades, these activities have contributed to declining sea turtle populations. The waters around Spain serve as important staging areas for sea turtles, particularly Caretta caretta, which spend part of their life cycle there. However, these same waters threaten turtles because of various causes of stranding. This study aims to comprehensively understand the rehabilitation process for these animals at the Wildlife Rehabilitation Center (WRC) La Tahonilla in Tenerife, Canary Islands. It also seeks to explore rehabilitation efforts at different centers focused on recovering sea turtles in both the mainland and the Canary Islands. Additionally, we have examined the procedures for addressing stranded sea turtles where a recovery center does not exist. Our findings reveal the existence of varying protocols among different centers in Spain’s mainland and islands. Improving and unifying these protocols is essential for enhancing the rehabilitation of sea turtles in Spain. Full article
(This article belongs to the Special Issue Feature Papers of Ecologies 2024)
Show Figures

Figure 1

Figure 1
<p>Map of the Canary Archipelago. In the middle of the picture appears the Island of Tenerife and the WRC “La Tahonilla”. Own source obtained from QGIS 3.36.3.</p>
Full article ">Figure 2
<p>Aerial view of the WRC “La Tahonilla”. Center of picture represents Z1 and above is the row of Z2 tanks.</p>
Full article ">Figure 3
<p>Image top left: turtle in random swimming. Image top right: turtle in swimming pool. Image bottom left: turtle resting. Image bottom right: turtle in patterned swimming (if the movement is repeated three times).</p>
Full article ">Figure 4
<p>Map of the strandings of turtles undergoing rehabilitation at the WRC “La Tahonilla” from February–May 2024. Elaborate from QGIS 3.36.3.</p>
Full article ">Figure 5
<p>Evolution of % resting, % swimming with patterns, and % random swimming in turtles in rehabilitation during their period at the center. The blue line indicates the trend.</p>
Full article ">Figure A1
<p>Causes and subcauses of stranding of individuals admitted to WRC “La Tahonilla” during the study period February–May 2024.</p>
Full article ">
15 pages, 4931 KiB  
Article
Water Hyacinth Invasion and Management in a Tropical Hydroelectric Reservoir: Insights from Random Forest and SVM Classification
by Luis Fernando Correa-Mejía and Yeison Alberto Garcés-Gómez
Ecologies 2025, 6(1), 8; https://doi.org/10.3390/ecologies6010008 - 23 Jan 2025
Viewed by 699
Abstract
The rapid proliferation of water hyacinth (Eichhornia crassipes) in newly formed reservoirs poses a significant threat to aquatic ecosystems and hydroelectric operations. The objective of this study was to map and monitor the spatio-temporal distribution of water hyacinth in the Hidroituango [...] Read more.
The rapid proliferation of water hyacinth (Eichhornia crassipes) in newly formed reservoirs poses a significant threat to aquatic ecosystems and hydroelectric operations. The objective of this study was to map and monitor the spatio-temporal distribution of water hyacinth in the Hidroituango reservoir in Colombia from 2018 to 2023, using Sentinel-2 satellite imagery and machine learning algorithms. The Random Forest (RF) and Support Vector Machine (SVM) algorithms were employed for image classification, and their performance was evaluated using various accuracy metrics. The results revealed that both algorithms effectively detected and mapped water hyacinth infestations, with RF demonstrating greater stability in capturing long-term trends and SVM exhibiting higher sensitivity to rapid changes in coverage. The study also highlighted the impact of the COVID-19 pandemic on control efforts, leading to a temporary increase in infestation. The findings underscore the importance of continuous monitoring and adaptive management strategies to mitigate the ecological and economic impacts of water hyacinth in the Hidroituango reservoir and similar environments. Full article
Show Figures

Figure 1

Figure 1
<p>General location map of Hidroituango reservoir. Department of Antioquia, Colombia.</p>
Full article ">Figure 2
<p>A methodology for mapping the spatio-temporal distribution of water hyacinth in the Hidroituango reservoir using the RF and SVM algorithms.</p>
Full article ">Figure 3
<p>Mapping results obtained after applying the RF algorithm to the Sentinel 2 images, in each of the periods evaluated between 2018 and 2023. The area shown corresponds to a hotspot of reservoir infestation during all seasons.</p>
Full article ">Figure 4
<p>Mapping results obtained after applying the SVM algorithm to the Sentinel 2 images, in each of the periods evaluated between 2018 and 2023. The area shown corresponds to a hotspot of reservoir infestation during all seasons.</p>
Full article ">Figure 5
<p>Percentage of area estimated by RF for each coverage within the reservoir.</p>
Full article ">Figure 6
<p>Percentage of area estimated by SVM for each coverage within the reservoir.</p>
Full article ">
23 pages, 3967 KiB  
Article
Distribution and Diversity of Myxomycetes Along the Elevational Belt of Mt. Calavite Wildlife Sanctuary (MCWS), Occidental Mindoro, Philippines
by Christon Jairus M. Racoma, John Carlo Redeña-Santos and Nikki Heherson A. Dagamac
Ecologies 2025, 6(1), 7; https://doi.org/10.3390/ecologies6010007 - 17 Jan 2025
Viewed by 800
Abstract
Myxomycetes are protists that predate microbial communities in soil and are heavily affected by changing climate conditions. As seen in a more distinct guild of myxomycete, their fructification diversity depends not only on the heterogeneity of vegetation but also on temperature and precipitation. [...] Read more.
Myxomycetes are protists that predate microbial communities in soil and are heavily affected by changing climate conditions. As seen in a more distinct guild of myxomycete, their fructification diversity depends not only on the heterogeneity of vegetation but also on temperature and precipitation. To determine the reverse pattern of microbial diversity established in temperate ecozones, foliar and lignicolous litters were collected along a tropical montane site in the Philippines. Fifty-seven (57) morphospecies of myxomycetes from 15 genera were determined. Alpha-diversity analysis revealed a significant decline in species richness and diversity with increasing elevation. Beta-diversity analysis, integrating non-metric multidimensional scaling (NMDS), PERMANOVA, and hierarchical clustering, revealed the complex relationships between species turnover and community composition across elevational gradients. These results conform to the hypothesis that species richness decreases as elevation increases, supporting that tropical ecozones follow the general trend of myxomycete diversity that was first observed in the temperate ecozones. The strong role of elevation in shaping myxomycete community structure is further emphasized. This indicates that conservation management efforts should become more stringent in the areas found at the lower elevation of a tropical montane forest, which are more ecologically sensitive to human-induced stressors and climate-related pressures. Full article
(This article belongs to the Special Issue Feature Papers of Ecologies 2024)
Show Figures

Figure 1

Figure 1
<p>Study area map of Mount Calavite Wildlife Sanctuary, Occidental Mindoro, showing the elevational gradient and the sampling points collected during the wet season in the months of August to October and the dry season in the months of March to May.</p>
Full article ">Figure 2
<p>Species accumulation curves (SACs) of myxomycetes composition on MWCS across different (<b>a</b>) seasonal collections, (<b>b</b>) substrate types, and (<b>c</b>) elevational gradients. Shaded areas indicate confidence intervals (conf = 0.95) for the estimates. Sampling completeness—seasonal collection: dry (63.43%) and wet (54.83%); substrate types: aerial (38.16%), ground (61.10%), and wood (42.83%); elevational gradient: elevation 1 (23.22%), elevation 2 (39.37%), elevation 3 (70.86%), elevation 4 (73.18%), and elevation five (95.02%).</p>
Full article ">Figure 3
<p>Rank abundance curve plots based on the abundance of species for different substrate types (aerial, ground, and wood), seasons (wet and dry), and elevational ranges (elevations 1, 2, 3, 4, and 5) testing five distribution models; thickened line represents best-fitting curve—Zipf model: shows how few species dominate in abundance, while many are rare; Mandelbrot model: shows where dominant species flatten in abundance and rare species decline sharply [<a href="#B51-ecologies-06-00007" class="html-bibr">51</a>]; Preemption model: competitive species dominate initially due to abiotic factors, while subsequent species’ abundances are influenced by competition [<a href="#B52-ecologies-06-00007" class="html-bibr">52</a>,<a href="#B53-ecologies-06-00007" class="html-bibr">53</a>].</p>
Full article ">Figure 4
<p>Alpha-diversity violin plots showing the comparison of four different diversity indices (Shannon’s index; Simpson’s index; Shannon Exponential; Inverse Simpson) in relation to season (<b>left column</b>), substrate type (<b>middle column</b>), and elevational range (<b>right column</b>).</p>
Full article ">Figure 5
<p>Non-metric multidimensional scaling (NMDS) ordination plot of myxomycetes species composition across different seasons, substrate types, and elevational ranges; ellipses represent 95% confidence intervals around per group; stress plot showing the relationship between observed dissimilarities and ordination distances from the NMDS analysis (k = 2); red line shows a smoothed fit, non-metric fit (R<sup>2</sup> = 0.976), and linear fit (R<sup>2</sup> = 0.93).</p>
Full article ">Figure 6
<p>Neighbor-joining clustering tree based on species composition (species and abundances) utilizing Bray–Curtis dissimilarity (CCC = 0.9678) and Jaccard similarity distances (CCC = 0.8226); Monte-Carlo plot simulating the hypotheses—species decreases as elevation increases—and mid-domain hypothesis.</p>
Full article ">
14 pages, 3436 KiB  
Article
Assessing the Economic and Ecological Costs of Human–Wildlife Conflict in Nuwara Eliya
by Mahanayakage Chamindha Anuruddha, Takehiro Morimoto, Saman Gamage and Faiz Marikar
Ecologies 2025, 6(1), 6; https://doi.org/10.3390/ecologies6010006 - 13 Jan 2025
Viewed by 966
Abstract
Human–wildlife conflict (HWC) is a growing concern in the Nuwara Eliya Divisional Secretariat Division (DSD) in the central highlands of Sri Lanka. This study investigates the nature and distribution of HWC, with particular focus on agricultural damage, livestock losses, infrastructure destruction, and human [...] Read more.
Human–wildlife conflict (HWC) is a growing concern in the Nuwara Eliya Divisional Secretariat Division (DSD) in the central highlands of Sri Lanka. This study investigates the nature and distribution of HWC, with particular focus on agricultural damage, livestock losses, infrastructure destruction, and human injuries. Data were collected through field surveys, expert opinions, satellite imagery, and census data, including interviews with 720 farmers (conducted between 2021 and 2022) and 25 online questionnaires, which provided expert insights on HWC. Animals such as wild boars, bandicoots, barking deer, toque macaques, porcupines, buffaloes, sambar, and leopards were found to be key to HWC, contributing to crop raiding, livestock predation, and infrastructure damage, and through the analytical hierarchy process (AHP), the wild boar was determined to have the greatest impact. Spatial analysis revealed conflict hotspots near forest and tea plantation boundaries, emphasizing the influence of land use and proximity to wildlife habitats. Mitigation strategies were explored; most farmers utilize multiple conflict reduction strategies, with varying efficacy. These findings underline the importance of developing region-specific strategies for HWC management, promoting sustainable agricultural practices, and fostering coexistence between wildlife and local communities. Full article
Show Figures

Figure 1

Figure 1
<p>Location map of the study area. (<b>a</b>) Map of South Asia, (<b>b</b>) location of the Nuwara Eliya DSD, and (<b>c</b>) Nuwara Eliya DSD Source: Sri Lanka Survey Department.</p>
Full article ">Figure 2
<p>LULC in Nuwara Eliya DSD.</p>
Full article ">Figure 3
<p>Types of animal damage reported within the study area.</p>
Full article ">Figure 4
<p>Wildlife species responsible for livestock damage, human casualties, crop raiding, and infrastructure damage in Nuwara Eliya DSD.</p>
Full article ">Figure 5
<p>Distribution of HWC: (<b>a</b>) crop damage distribution, (<b>b</b>) livestock damage distribution, (<b>c</b>) infrastructure damage distribution, and (<b>d</b>) distribution of animal attacks on humans.</p>
Full article ">Figure 6
<p>HWC distribution with forest and tea areas in Nuwara Eliya DSD: (<b>a</b>) crop damage distribution, (<b>b</b>) livestock damage distribution, (<b>c</b>) infrastructure damage distribution, and (<b>d</b>) distribution of animal attacks on humans.</p>
Full article ">Figure 7
<p>Distribution of overall HWC based on AHP and MCDA; HWC = (BD*0.17+BA*0.20+WB*0.26+PO*0.13+MA*0.16+BU0.09+SA*0.07+LE*0.07).</p>
Full article ">Figure 8
<p>Types of crop damage mitigation methods.</p>
Full article ">
20 pages, 2078 KiB  
Article
Distribution Patterns and Habitat Preferences of Five Globally Threatened and Endemic Montane Orthoptera (Parnassiana and Oropodisma)
by Apostolis Stefanidis, Konstantinos Kougioumoutzis, Konstantina Zografou, Georgios Fotiadis, Luc Willemse, Olga Tzortzakaki and Vassiliki Kati
Ecologies 2025, 6(1), 5; https://doi.org/10.3390/ecologies6010005 - 11 Jan 2025
Viewed by 1425
Abstract
Greece is a European hotspot for Orthoptera (378 species), yet it has been scarcely explored. We investigated the distribution and habitat preferences of the species of two endemic Orthoptera genera, Parnassiana and Oropodisma, in the montane ecosystems of central Greece. We conducted [...] Read more.
Greece is a European hotspot for Orthoptera (378 species), yet it has been scarcely explored. We investigated the distribution and habitat preferences of the species of two endemic Orthoptera genera, Parnassiana and Oropodisma, in the montane ecosystems of central Greece. We conducted field surveys from 2021 to 2024 in 174 sites across seven mountains. The species of both genera preferred habitats above 1500 m, with species-specific preferences for microhabitat parameters: Parnassiana species favored moderate slopes with dense shrub cover, while Oropodisma species favored substrates with intermediate stone cover and relatively high vegetation cover. Species distribution models estimated the area of suitable habitat for Parnassiana to be at 5 km2 and Oropodisma at 3.28 km2. The Normalized Difference Vegetation Index (NDVI) and potential evapotranspiration were the key environmental drivers of the habitat suitability for both genera. Generalized regression models showed that altitude positively influenced Parnassiana population density, peaking at 2200 m, whereas rock and soil cover negatively impacted Oropodisma population densities. The results emphasize the critical role of montane habitats in sustaining these species and provide essential data for future research and conservation strategies. Full article
Show Figures

Figure 1

Figure 1
<p>Study area across the distribution ranges of the two genera complexes (including seven mountains) and localities visited in the period of 2021–2024.</p>
Full article ">Figure 2
<p>Habitat suitability maps for the target genera within their potential distribution areas. Panel (<b>a</b>) illustrates the habitat suitability for the <span class="html-italic">Oropodisma</span> genus and panel (<b>b</b>) shows the habitat suitability for the <span class="html-italic">Parnassiana</span> genus. The maps depict continuous habitat suitability values.</p>
Full article ">
7 pages, 1225 KiB  
Communication
The Interspecific Abundance–Occupancy Relationship in Invertebrate Metacommunities Associated with Intertidal Mussel Patches
by Ricardo A. Scrosati
Ecologies 2025, 6(1), 4; https://doi.org/10.3390/ecologies6010004 - 3 Jan 2025
Viewed by 842
Abstract
To explain the distribution and abundance of species, ecology searches for general models. A pattern often encountered in nature is the interspecific abundance–occupancy relationship (AOR), which describes how the mean local abundance of species relates to the proportion of local sites that each [...] Read more.
To explain the distribution and abundance of species, ecology searches for general models. A pattern often encountered in nature is the interspecific abundance–occupancy relationship (AOR), which describes how the mean local abundance of species relates to the proportion of local sites that each species occupies. Both are central variables in ecology and are often positively correlated, although exceptions have been found. As most AOR research has been conducted with terrestrial systems, recent studies are testing for its occurrence in marine systems. This contribution tests the AOR for invertebrate metacommunities associated with intertidal mussel patches. Using data from six coastal locations in Nova Scotia (Canada), this study shows that the negative binomial model properly describes the relationship between abundance and occupancy for these systems. The degree of wave exposure (wave-sheltered versus wave-exposed habitats) had some influence on the shape of the AOR. Overall, these findings extend the applicability of the AOR to intertidal invertebrate metacommunities. The raw data are included as part of this article to help future syntheses on the AOR, which will need data for a variety of terrestrial and aquatic environments. Full article
Show Figures

Figure 1

Figure 1
<p>Map of Nova Scotia indicating the six surveyed intertidal locations.</p>
Full article ">Figure 2
<p>Abundance–occupancy relationship (with a 95% confidence band) for each of the six surveyed locations (invertebrate metacommunities). Each dot represents a single invertebrate species. For each species, abundance (<span class="html-italic">µ</span>) represents the mean number of individuals per mussel patch (per dm<sup>2</sup>) averaged over the 15 patches surveyed at each location, while occupancy (<span class="html-italic">P</span>) represents the proportion of the 15 surveyed mussel patches where the invertebrate species in question was present.</p>
Full article ">
13 pages, 928 KiB  
Article
A Conceptual Framework for the Apibotanical Evaluation of Different Landscapes
by Rosana Díaz, Silvina Niell, María Verónica Cesio and Horacio Heinzen
Ecologies 2025, 6(1), 3; https://doi.org/10.3390/ecologies6010003 - 30 Dec 2024
Viewed by 592
Abstract
The suitability of different agroecosystems (native forest, soybean, artificial forest with Eucalyptus sp., mixed horticulture and fruticulture, and dairy prairies) for settling and managing hives for honey production were appraised via holistic surveys of the spatial and seasonal occurrence of floral resources. Metadata [...] Read more.
The suitability of different agroecosystems (native forest, soybean, artificial forest with Eucalyptus sp., mixed horticulture and fruticulture, and dairy prairies) for settling and managing hives for honey production were appraised via holistic surveys of the spatial and seasonal occurrence of floral resources. Metadata were obtained from a project developed by our group, which took place between 2014 and 2017. Species richness, abundance, growth habit (tree, shrub, stand, scrub or stem, accompanying species), and the flowering period for each melliferous plant across the different seasons in 120 samples were measured. Using the Shannon–Wiener diversity index and the floral characteristics of the different species in each environment, an Agroecosystem Apibotanical Index was developed. It revealed that the best agroecosystems for honey production were the most biodiverse native forest as well as mixed horticulture and fruit culture. Knowledge of the floral characteristics and species arrangement enabled the categorization of agroecosystems, aiming for rational management to enhance honey production. Full article
Show Figures

Figure 1

Figure 1
<p>Rank–abundance curves of floral species in the five agroecosystems (left up-) artificial forest, (right up) mixed horticulture and fruticulture, (left middle) native forest, (right middle) dairy prairies, and (left up) soybean per patch (1, 2, 3), with the abundance axis being in relative terms. In its construction, the range of the species (on the abscissa axis) and the percentage of accumulated abundance (on the ordinate axis) were used. The Vegan package (R) and radfit function were used.</p>
Full article ">Figure 2
<p>Seasonal production of honey in the different landscapes. Agroecosystems: D: dairy prairies; AF: artificial <span class="html-italic">Eucalyptus</span> sp. forest; HF: mixed horticulture and fruticulture; S: soybean crop; NF: native forest.</p>
Full article ">
29 pages, 4701 KiB  
Article
Assessment of Spatial Dynamics of Forest Cover in Lomami National Park (DR Congo), 2008–2024: Implications for Conservation and Sustainable Ecosystem Management
by Gloire Mukaku Kazadi, Médard Mpanda Mukenza, John Kikuni Tchowa, François Malaisse, Célestin Kabongo Kabeya, Jean-Pierre Pitchou Meniko To Hulu, Jan Bogaert and Yannick Useni Sikuzani
Ecologies 2025, 6(1), 2; https://doi.org/10.3390/ecologies6010002 - 29 Dec 2024
Viewed by 923
Abstract
Lomami National Park, located in the Democratic Republic of the Congo (DR Congo), is renowned for the integrity of its forest ecosystems, safeguarded by the absence of agricultural activities and limited road access. However, these ecosystems remain under-researched, particularly in terms of forest [...] Read more.
Lomami National Park, located in the Democratic Republic of the Congo (DR Congo), is renowned for the integrity of its forest ecosystems, safeguarded by the absence of agricultural activities and limited road access. However, these ecosystems remain under-researched, particularly in terms of forest cover dynamics. This research gap poses a significant challenge to establishing rigorous monitoring systems, which are essential for ensuring the long-term preservation of these valuable ecosystems. This study utilized Google Earth Engine to preprocess Landsat images from 2008, 2016, and 2024, employing techniques such as atmospheric correction and cloud masking. Random Forest classification was applied to analyze land cover changes, using training datasets curated through ground-truthing and region-of-interest selection. The classification accuracy was evaluated using metrics such as overall accuracy, producer’s accuracy, and user’s accuracy. To assess landscape configuration, metrics such as class area, patch number, largest patch index, disturbance index, aggregation index, and edge density were calculated, distinguishing between the park’s core and peripheral zones. Spatial transformation processes were analyzed using a decision tree approach. The results revealed a striking contrast in forest cover stability between Lomami National Park and its surrounding periphery. Within the park, forest cover has been preserved and even showed a modest increase, rising from 92.60% in 2008 to 92.75% in 2024. In contrast, the peripheral zone experienced a significant decline in forest cover, decreasing from 79.32% to 70.48% during the same period. This stability within the park extends beyond maintaining forested areas; it includes preserving and enhancing the spatial structure of forest ecosystems. For example, edge density, a key indicator of forest edge compactness, remained stable in the park, fluctuating between 8 m/ha and 9 m/ha. Conversely, edge density in the peripheral zone exceeded 35 m/ha, indicating that forest edges within the park are considerably more cohesive and intact than those in the surrounding areas. The spatial transformation processes also underscored these contrasting dynamics. In the park, the primary process was the aggregation of primary forest patches, reflecting a trend toward continuous and connected forest landscapes. By contrast, the peripheral zone exhibited dissection, indicating fragmentation and the breakdown of forest patches. These findings highlight the park’s critical role in maintaining both the extent and structural integrity of forest ecosystems, setting it apart from the more degraded periphery. They underscore the resilience of forest ecosystems in the face of limited anthropogenic pressures and the crucial importance of effective land management and rigorous conservation strategies in addressing the challenges posed by urbanization and rural expansion. Additionally, the results emphasize that well-adapted conservation measures, combined with specific demographic and socio-economic conditions, can play a pivotal role in achieving long-term forest preservation and ecological stability. Full article
Show Figures

Figure 1

Figure 1
<p>Geographical location of the Lomami National Park (protected area). The park is in the Maniema and Tshopo provinces, in DR Congo (<b>A</b>). The park covers a total area of 30,000 km<sup>2</sup> and is attached to a densely populated peripheral zone, including the city of Kindu (<b>B</b>). The red box indicates the location of the study area in DR Congo.</p>
Full article ">Figure 2
<p>A diagram representing the ten processes of spatial transformation derived from thirteen common types of spatial configurations or geometries in a binary landscape. Adapted from Bogaert et al. [<a href="#B74-ecologies-06-00002" class="html-bibr">74</a>]. (1) Fragmentation: landscape conversion through the disruption of continuity into five disconnected patches of unequal sizes and shapes; (2) Perforation: transformation by the formation of four holes; (3) Dissection: subdivision of a continuous area by uniformly wide lines of small dimensions; (4) Shrinkage: reduction in patch size; (5) Attrition: disappearance of one of the patches present in the original landscape; (6) Creation: transformation of the landscape by the formation of a new patch, in-creasing the number of patches from two to three; (7) Deformation: transformation characterized by the change in shape of two patches into a rectangular form without a change in area; (8) Shift: translocation of one of the two patches; (9) Enlargement: transformation through the increase in size of both patches; (10) Aggregation: merging of patches.</p>
Full article ">Figure 3
<p>Mapping of land cover changes in Lomami National Park and its peripheral zone between 2008, 2016, and 2024, derived from supervised classifications of Landsat images using the Random Forest algorithm.</p>
Full article ">Figure 4
<p>Evolution of the total area of land cover classes in the Lomami National Park and its periphery zone 2008 and 2024. The total areas are 30,879 km<sup>2</sup> for the protected zone and 12,686.05 km<sup>2</sup> for the periphery. MUAL: mixed urban and agricultural land.</p>
Full article ">Figure 5
<p>Evolution of the disturbance index in the Lomami National Park and its peripheral zone between 2008 and 2024. Disturbance index quantifies human-induced disturbances, providing insight into anthropogenic pressure.</p>
Full article ">Figure 6
<p>Evolution of aggregation index and edge density in the Lomami National Park and its peripheral zone between 2008 and 2024. Edge density measures the total edge length of patches per unit area, highlighting fragmentation levels. Aggregation index reflects the degree to which similar patches are clumped together, indicating landscape connectivity.</p>
Full article ">Figure 7
<p>Illustration of the spatial transformation process identified within the Lomami National Park and its surrounding zone.</p>
Full article ">Figure A1
<p>Spectral signature (average of classified Landsat images of 2008, 2016, and 2024) of land cover classes within the Lomami National Park and its surrounding areas across the green, red, and near-infrared spectral bands. R (Red), G (Green) and NIR (near-infrared).</p>
Full article ">
18 pages, 3164 KiB  
Article
Winter Diet Pattern of Snow Leopard and Factors Affecting Livestock Depredation in Nubri Valley of Manaslu Conservation Area, Nepal
by Sachet Timilsina, Bishnu Prasad Pandey, Bijaya Neupane, Bishnu Prasad Bhattarai, Thakur Silwal, Ajit Tumbahangphe, Ashok Subedi, Ganesh Pant, Zdenka Krenova and Bikram Shrestha
Ecologies 2025, 6(1), 1; https://doi.org/10.3390/ecologies6010001 - 26 Dec 2024
Viewed by 1899
Abstract
Limited information exists on the diet of snow leopards (SL), factors affecting livestock mortality, and local attitudes toward SL conservation in the Manaslu Conservation Area (MCA), Nepal. Therefore, we aim to investigate the dietary preferences of SL, the factors influencing livestock mortality, and [...] Read more.
Limited information exists on the diet of snow leopards (SL), factors affecting livestock mortality, and local attitudes toward SL conservation in the Manaslu Conservation Area (MCA), Nepal. Therefore, we aim to investigate the dietary preferences of SL, the factors influencing livestock mortality, and local conservation attitudes. From November 2021 to January 2022, 23 SL scats were collected along 24 transects (total length: 21.6 km) in MCA. Camera traps, set within 4 km × 4 km grids at 28 stations for 661 trap nights, were used to assess prey availability. Jacobs’ index calculated prey preference, while a Generalized Linear Mixed Model (GLMM) assessed factors linked to livestock depredation. Additionally, 65 households from two villages were randomly selected in a survey on depredation and conservation attitudes. Scat analysis identified six wild prey species, including pika (Ochotona sp.), Himalayan tahr (Hemitragus jemlahicus), and blue sheep (Pseudois nayaur), as well as three domestic species: ox/cow, yak, and horse. Himalayan tahr had the highest presence in the SL diet (40%). Despite pika having the highest Relative Abundance Index (RAI), SL strongly preferred horses and avoided pika. Larger prey, such as horses, Himalayan tahr, and blue sheep, were highly preferred. Households with more livestock experienced higher depredation rates. Local attitudes toward SL conservation were generally positive, with an average score of 2.59. We recommend an integrated SL conservation plan in MCA, incorporating local participation, income diversification, and employment programs to mitigate conflicts and promote coexistence. Full article
Show Figures

Figure 1

Figure 1
<p>Map of study area showing camera trap locations of Nubri Valley.</p>
Full article ">Figure 2
<p>(<b>a</b>,<b>b</b>) Two snow leopard individuals captured by camera trap at different locations in the study area. Photo credit: Bikram Shrestha and Sachet Timilsina.</p>
Full article ">Figure 3
<p>Diet composition of snow leopards in Nubri Valley of Manaslu Conservation Area.</p>
Full article ">Figure 4
<p>Cumulative frequency of occurrence of prey species of snow leopard.</p>
Full article ">Figure 5
<p>Prey selection by snow leopards in Nubri Valley.</p>
Full article ">Figure 6
<p>Education category status of respondents.</p>
Full article ">
Previous Issue
Back to TopTop