27 research outputs found

    Phytoindication assessment of the effect of reconstruction on the light regime of an urban park

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    The ecological restoration of urban parks is used to increase their recreational attractiveness, improve air quality, mitigate urban heat island effects, improve stormwater infiltration, and provide other social and environmental benefits. The dynamics of plant communities after urban forest restoration requires investigation. The study assessed the impact of urban park reconstruction on the state of grass cover, phytoindication of changes in light regime caused by park reconstruction and found out the dependence of reliability of phytoindication assessment on the number of species in the relevant area. The study was conducted in the recreational area of the Botanical Garden of the Oles Honchar Dnipro National University (Ukraine). A tree plantation was created after the Second World War in the location of a natural oak forest. In 2019, a 2.8 ha area of the park was reconstructed. The samples were taken within polygons, two of which were placed in the reconstruction area and two of which were placed in a similar section of the park where no reconstruction was performed. During the reconstruction process, walkways were rebuilt, shrubs were removed, old, damaged trees were removed, and tree crowns were trimmed. Juvenile trees were planted in place of the removed old trees. Old outbuildings, which greatly impaired the aesthetic perception of the park, were also removed. Transport and construction machinery was involved in the reconstruction. A total of 65 plant species were found within the studied polygons. The number of herbaceous species in the park area after reconstruction was higher than without reconstruction. The crown closure in the reconstructed area was significantly lower than that in the untreated conditions. The phytoindication assessment showed that the light regime varies from the conditions suitable for the scyophytes (plants of typical foliage forests) to the conditions suitable for the sub-heliophytes (plants of light forests and shrubberies, or high herbaceous communities; lower layers are in the shade). The light regime in the park area after reconstruction was statistically significantly different from the regime in the untreated park area. The lighting regime after the reconstruction was favourable to sub-heliophytes, and without reconstruction the regime favoured hemi-scyophytes. Tree canopy crown closure negatively correlated with grass height and herbaceous layer projective cover. The tree canopy crown closure, grass height, and herbaceous layer projective cover were able to explain 86% of the phytoindication assessment of the lighting regime variation. These parameters negatively affected the light regime. The prospect of further research is to investigate the dependence of indicative reliability of the assessment of other environmental factors with the help of phytoindication depending on the number of species. In addition to the indication of traditional ecological factors it is of particular interest to clarify the aspect of the dynamics of hemeroby indicators as a result of park reconstruction

    Anthropogenic load Ρ–s a leading factor in the morphological variability of Chondrula tridens (Gastropoda, Enidae) in the northwestern Azov Sea region

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    Morphometric data are widely used in biology to assess intraspecific and inter-population variability and for bioindication and environmental condition assessment. The following hypotheses have been experimentally tested in the paper: 1) the vegetation type affects the change in the shell shape of Chondrula tridens martynovi Gural-Sverlova & Gural, 2010; 2) the change in the shell shape of this species is influenced by the biotope moisture regime; 3) the shell shape changes depending on the anthropogenic load level. The material in the form of empty, fully formed Ch. tridens shells was collected in 2019 in the north-western Azov region within the basin of the Molochna River. The collection points were located in settlements and outside them and differed in vegetation, moisture regime and level of anthropogenic load. The vegetation has been expertly attributed to two alternative types: herbaceous vegetation and tree plantations. By moisture level, the locations have been assessed as xerophytic and mesoxerophytic. The anthropogenic load levels have been assessed as low, medium and high. The study revealed that the morphological characteristics of Ch. tridens demonstrate a significant component of variability, which is due to the shell size. The shell size depends on the anthropogenic impact level. Under conditions of high anthropogenic impact, the shell size increases. Mollusks from locations with low and medium anthropogenic impact levels did not differ in shell size. After extraction of the size component, morphological properties develop three main trends of variability. The mouth apparatus development of mollusks does not depend on the vegetation type, but depends on the biotope moisture level and the anthropogenic transformation level. The mollusk shell elongation was observed to have the opposite dynamics of the height parameters in relation to the width and depended on the level of anthropogenic load. Rearrangement in the mouth apparatus depended on the biotope moisture level and the anthropogenic load level. There were distinguished four clusters, the quantitative morphological features of which allowed us to identify them as morphotypes. Each location was characterized by a combination of different morphotypes, according to which the sampling points may be classified. Morphotype 1 corresponds to biotopes with low level of anthropogenic load, morphotype 4 corresponded to biotopes with high anthropogenic load. Morphotypes 2 and 3 corresponded to moderate level of anthropogenic load. Vegetation type is not an important factor in determining the morphotypic diversity of populations. Under xerophytic conditions, morphotypes 2 and 3 are more common, and under mesoxerophytic conditions, morphotypes 1 and 4 are more common. The range of molluscs in different habitats needs to be expanded in the future to clarify climatic and other patterns

    The small-scale variation of herb-layer community structure in a riparian mixed forest

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    The ground vegetation layer is the most diverse plant community in forest ecosystems. We have shown the role of spatial variables, soil properties and overstorey structure in spatial variation of the herb-layer community in a riparian mixed forest . The research was conducted in the "Dnipro-Orils’kiy" Nature Reserve (Ukraine). The research polygon was located in the forest in the floodplain of the River Protich, which is a left tributary of the River Dnipro. Plant abundance was quantified by measuring cover within an experimental polygon. The experimental polygon consisted of 7 transects, each comprising 15 test points. The distance between the rows in the site was 3 m. At the site we established a plot of 45 Γ— 21 m, with 105 subplots of 3 Γ— 3 m organized in a regular grid. A list of vascular plant species was composed for each 3 Γ— 3 m subplot along with visual estimates of species cover projection. The plant community was represented by 43 species, of which 18.6% were phanerophytes, 39.5% were hemicryptophytes, 9.3% were therophytes, 7.0% were geophytes. An overall test of random labelling revealed the total nonrandom distribution of the tree stems within the site. The species-specific test of random labelling showed the nonrandom segregated distribution of Acer tataricum, Pyrus communis, Quercus robur, and Ulmus laevis. Crataegus monogyna and Euonymus europaeus were distributed randomly. The nearest neighbour of Acer tataricum was less likely to be Ulmus laevis. There was no direct spatial connection between Acer tataricum and other trees. Crataegus monogyna, Pyrus communis, Quercus robur and Euonymus europaeus were not segregated from all other species. The nearest neighbour of Ulmus laevis was less likely to be Acer tataricum. Constrained correspondence analysis (CCA) was applied as ordination approach. The forward selection procedure allowed us to select 6 soil variables which explain 28.3% of the herb-layer community variability. The list of the important soil variables includes soil mechanical impedance (at the depth 0–5, 30–35, 75–80, and 95–10 cm), soil moisture, and soil bulk density. The variation explained by pure spatial variables accounted for 11.0 %. The majority of the tree-distance structured variation in plant community composition was broad-scaled. The spatial scalograms were left-skewed asymmetric. Significant relationship was found between the pure spatial component of the community variation and a number of phytoindicator estimations, most important of which were the variability of damping and humidity. Tree stand was obseerved to be a considerable factor structuring both the herb-layer community and spatial variation of the physical properties of soil

    Phytoindication assessment of the effect of reconstruction on the light regime of an urban park

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    The ecological restoration of urban parks is used to increase their recreational attractiveness, improve air quality, mitigate urban heat island effects, improve stormwater infiltration, and provide other social and environmental benefits. The dynamics of plant communities after urban forest restoration requires investigation. The study assessed the impact of urban park reconstruction on the state of grass cover, phytoindication of changes in light regime caused by park reconstruction and found out the dependence of reliability of phytoindication assessment on the number of species in the relevant area. The study was conducted in the recreational area of the Botanical Garden of the Oles Honchar Dnipro National University (Ukraine). A tree plantation was created after the Second World War in the location of a natural oak forest. In 2019, a 2.8 ha area of the park was reconstructed. The samples were taken within polygons, two of which were placed in the reconstruction area and two of which were placed in a similar section of the park where no reconstruction was performed. During the reconstruction process, walkways were rebuilt, shrubs were removed, old, damaged trees were removed, and tree crowns were trimmed. Juvenile trees were planted in place of the removed old trees. Old outbuildings, which greatly impaired the aesthetic perception of the park, were also removed. Transport and construction machinery was involved in the reconstruction. A total of 65 plant species were found within the studied polygons. The number of herbaceous species in the park area after reconstruction was higher than without reconstruction. The crown closure in the reconstructed area was significantly lower than that in the untreated conditions. The phytoindication assessment showed that the light regime varies from the conditions suitable for the scyophytes (plants of typical foliage forests) to the conditions suitable for the sub-heliophytes (plants of light forests and shrubberies, or high herbaceous communities; lower layers are in the shade). The light regime in the park area after reconstruction was statistically significantly different from the regime in the untreated park area. The lighting regime after the reconstruction was favourable to sub-heliophytes, and without reconstruction the regime favoured hemi-scyophytes. Tree canopy crown closure negatively correlated with grass height and herbaceous layer projective cover. The tree canopy crown closure, grass height, and herbaceous layer projective cover were able to explain 86% of the phytoindication assessment of the lighting regime variation. These parameters negatively affected the light regime. The prospect of further research is to investigate the dependence of indicative reliability of the assessment of other environmental factors with the help of phytoindication depending on the number of species. In addition to the indication of traditional ecological factors it is of particular interest to clarify the aspect of the dynamics of hemeroby indicators as a result of park reconstruction. Keywords: recreation; diversity; indicator reliability; hemeroby; ecosystem transformation; plant community

    Ecological Niche Packing and Spatial Organisation of the Urban Park Macrofauna Comminity

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    Abstract. The results of studying of the spatial organization of the soil macrofauna of the urbanozem of the grassland were processed by OMI- and RLQ-analysis methods. The biogeocenotical situation at the location of an experimental polygon was shown to be typical of a meadow-steppe mega-mesotrophic xeromesophic character. The data for the research was collected by means of manual sorting of the soil samples with the area of 0.25Γ—25 cm on a regular grid (7Γ—15 samples) with the distance between the selection points 2 m (results presented as L-table), the measurement of temperature, electrical conductivity and soil penetration resistance, the litter depth and the height of the grass (R-table). The soil macrofauna of the experimental area was represented by 27 species with a total density of 56.38 ind./ΠΌ2. The ecological structure of the animal community of the soil was dominated by the pratants and silvants, mesophiles, olygotropic, endogeic topomorphs, saprophagous. Such edaphic characteristics as soil penetration resistance, electrical conductivity, litter depth, as well as height of grass, played an important role in structuring of ecological niche of macrofauna community. The first two axis of OMI analysis described 73.43% of inertia, which was sufficient for the description of the differentiation ecological niches of macrofauna on the investigated polygon to conduct in the space of the first two axes. For the average value of the marginality of the community (OMI = 2.90), the significance level was Ρ€ = 0.001, which testifies to the important role of the selected environment variables for structuring of the soil macrofauna community. The four key functional groups of macrofauna were found as a result, the RLQ-analysis and the next cluster procedure and assessed the role of the edaphic factors in their spatial variation. Each of the functional groups was interpreted in terms of an ecomorphic approach

    Temperature effect on the temporal dynamic of terrestrial invertebrates in technosols formed after reclamation at a post-mining site in Ukrainian steppe drylands

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    The research was carried out at the Research Centre of the Dnipro State Agrarian and Economic University in Pokrov city. Sampling was carried out in 2013–2015 on a variant of artificial soil (technosols) formed on loess-like loam, red-brown clay, green-grey clay, technological mixture of rocks, and also formed on loess-like loam with a humus-rich 70 cm top soil layer. To investigate the spatiotemporal variation in the abundance, species richness and species composition of invertebrate assemblages within the experimental polygon, the animals were sampled using pitfall traps. In total, 60 pitfall traps were operated simultaneously during each sampling period. Each year the pitfalls were emptied 26 times every 7–9 days. Invertebrates (Arthropoda and Mollusca) of 6 classes, 13 orders, 50 families and 202 species or parataxonomic units were recorded. Diplopoda was most abundant taxonomic group, though it was represented by only one species Rossiulus kessleri (Lohmander, 1927). Coleoptera and Araneae were the most numerous taxonomic groups. Readily available water for plants, precipitation, wind speed, atmospheric temperature (daily minimum, daily maximum, daily mean), atmospheric humidity and atmospheric pressure were used as environmental predictors. Two dimension geographic coordinates of the sampling locations were used to generate a set of orthogonal eigenvector-based spatial variables. Time series of sampling dates were used to generate a set of orthogonal eigenvector-based temporal variables. The moisture content in the technosols was revealed to be the most important factor determining the temporal dynamics of the terrestrial invertebrate community in conditions of semi-arid climate and the ecosystem which formed as a result of the reclamation process. Following soil moisture, the factor most strongly affecting invertebrates in the technosols was temperature. From the total set of the invertebrates, two relatively homogeneous species groups in terms of thermal preferences were extracted: the microtemperature and mesotemperature groups. The microtemperature species are more tolerant to the thermal factor, and the mesotemperature species are more sensitive. The Huisman-Olff-Fresco approach expanded by Jansen-Oksanen provides a wide set of ecologically relevant models which are able to explain species response. The species response to temperature is affected by a complex of other environmental, temporal and spatial factors. The effect of other factors on the species response must be previously extracted to find real estimations of the species temperature optima and tolerance. The approaches to solving this problem may be the object of future investigation

    Fitting competing models and evaluation of model parameters of the abundance distribution of the land snail Vallonia pulchella (Pulmonata, Valloniidae)

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    This paper summarizes the mechanisms behind the patterning of the intra-population abundance distribution of the land snail Vallonia pulchella (Mьller, 1774). The molluscs were collected in recultivated soil formed on red-brown clays (Pokrov, Ukraine). Data obtained in this study reveal that V. pulchella population abundance ranges from 1 to 13 individuals per 100 g of soil sample. To obtain estimates of the mean, three models were used: the model of the arithmetic mean, the Poisson model and a log-normal model. The arithmetic mean of the occurrence of this species during the study period was 1.84 individuals/sample. Estimation of the average number of molluscs in one sample calculated using the Poisson model is lower and equals 1.40 individuals/sample. The distribution of the number of individuals in a population was described by the graphics "rank – abundance". The individual sample plot sites with molluscs may be regarded as equivalents of individual species in the community. For the analysis, the following models were used: broken sticks model, niche preemption model, log-normal model, Zipf model, and Zipf-Mandelbrot model. Applying the log-normal distribution gives a lower estimate of the mean density at 1.28 individuals/sample. Median value and mode is estimated at 1.00 individuals/sample. The Zipf-Mandelbrot model was shown as the most adequate to describe distribution of the V. pulchella population within the study area. The Zipf-Mandelbrot model belongs to the family of so-called non-Gaussian distributions. This means that the sample statistics do not possess asymptotic properties and by increasing the sample size, they tend to infinity, and are not close to the values of the general population. Therefore, the average value of the random variable that describes the non-Gaussian distribution has no statistical meaning. From an environmental point of view, this means that within the study area the capacity of the habitat is large, and for some combination of environmental conditions the rapid growth of the abundance of a given species is possible

    ΠŸΡ€ΠΈΠΌΠ΅Π½Π΅Π½ΠΈΠ΅ Ξ²-Ρ„ΡƒΠ½ΠΊΡ†ΠΈΠΈ Π² Ρ„ΠΈΡ‚ΠΎΠΈΠ½Π΄ΠΈΠΊΠ°Ρ†ΠΈΠΈ для ΡƒΡ‡Π΅Ρ‚Π° асиммСтрии ΠΊΡ€ΠΈΠ²Ρ‹Ρ… ΠΎΡ‚ΠΊΠ»ΠΈΠΊΠ° Π²ΠΈΠ΄ΠΎΠ² растСний

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    Π’ Ρ€Π°Π±ΠΎΡ‚Π΅ ΠΏΡ€Π΅Π΄Π»ΠΎΠΆΠ΅Π½ ΠΏΠΎΠ΄Ρ…ΠΎΠ΄ для Ρ„ΠΈΡ‚ΠΎΠΈΠ½Π΄ΠΈΠΊΠ°Ρ†ΠΈΠΎΠ½Π½ΠΎΠΉ ΠΎΡ†Π΅Π½ΠΊΠΈ экологичСских Ρ„Π°ΠΊΡ‚ΠΎΡ€ΠΎΠ² Π½Π° основС Π΄ΠΈΠ°ΠΏΠ°Π·ΠΎΠ½Π°Π»ΡŒΠ½Ρ‹Ρ… шкал с ΡƒΡ‡Π΅Ρ‚ΠΎΠΌ Π·Π½Π°Ρ‡Π΅Π½ΠΈΠΉ ΠΊΠ°Ρ€Π΄ΠΈΠ½Π°Π»ΡŒΠ½Ρ‹Ρ… Ρ‚ΠΎΡ‡Π΅ΠΊ ΠΈ вСроятной асиммСтрии ΠΊΡ€ΠΈΠ²Ρ‹Ρ… ΠΎΡ‚ΠΊΠ»ΠΈΠΊΠ° Π²ΠΈΠ΄ΠΎΠ² растСний. ЭкологичСскиС Ρ„Π°ΠΊΡ‚ΠΎΡ€Ρ‹ ΠΌΠΎΠ΄Π΅Π»ΠΈΡ€ΡƒΡŽΡ‚ΡΡ Ρ„ΠΈΡ‚ΠΎΠΈΠ½Π΄ΠΈΠΊΠ°Ρ†ΠΈΠΎΠ½Π½Ρ‹ΠΌΠΈ шкалами, Π΄ΠΈΠ°ΠΏΠ°Π·ΠΎΠ½ Π²Π°Ρ€ΡŒΠΈΡ€ΠΎΠ²Π°Π½ΠΈΡ ΠΊΠΎΡ‚ΠΎΡ€Ρ‹Ρ… ΠΎΠ³Ρ€Π°Π½ΠΈΡ‡Π΅Π½. Π’ Ρ†Π΅Π½Ρ‚Ρ€Π°Π»ΡŒΠ½ΠΎΠΉ части Π΄ΠΈΠ°ΠΏΠ°Π·ΠΎΠ½Π° Ρ„Π°ΠΊΡ‚ΠΎΡ€Π° кривая ΠΎΡ‚ΠΊΠ»ΠΈΠΊΠ° Π²ΠΈΠ΄Π° ΠΈΠΌΠ΅Π΅Ρ‚ Ρ„ΠΎΡ€ΠΌΡƒ, ΠΊΠΎΡ‚ΠΎΡ€ΡƒΡŽ ΠΌΠΎΠΆΠ½ΠΎ Π½Π°Π΄Π΅ΠΆΠ½ΠΎ Π°ΠΏΠΏΡ€ΠΎΠΊΡΠΈΠΌΠΈΡ€ΠΎΠ²Π°Ρ‚ΡŒ Π½ΠΎΡ€ΠΌΠ°Π»ΡŒΠ½Ρ‹ΠΌ Π·Π°ΠΊΠΎΠ½ΠΎΠΌ Гаусса. Π­Ρ‚ΠΎ позволяСт ΠΏΠΎΠ»Π½ΠΎΡΡ‚ΡŒΡŽ обосновано с ΠΏΠΎΠΌΠΎΡ‰ΡŒΡŽ ΠΊΠ°Ρ€Π΄ΠΈΠ½Π°Π»ΡŒΠ½Ρ‹Ρ… Ρ‚ΠΎΡ‡Π΅ΠΊ, ΠΊΠΎΡ‚ΠΎΡ€Ρ‹Π΅ нСпосрСдствСнно ΠΎΠ±ΠΎΠ·Π½Π°Ρ‡Π°ΡŽΡ‚ΡΡ ΠΈΠ½Π΄ΠΈΠΊΠ°Ρ‚ΠΎΡ€Π½Ρ‹ΠΌΠΈ значСниями Π²ΠΈΠ΄Π°, Π²Ρ‹Ρ‡ΠΈΡΠ»ΡΡ‚ΡŒ ΠΎΡ†Π΅Π½ΠΊΠΈ экологичСского ΠΎΠΏΡ‚ΠΈΠΌΡƒΠΌΠ° Π²ΠΈΠ΄Π°. УсрСднСнныС значСния ΠΎΡ†Π΅Π½ΠΎΠΊ экологичСских ΠΎΠΏΡ‚ΠΈΠΌΡƒΠΌΠΎΠ² Π²ΠΈΠ΄ΠΎΠ² сообщСства, Π²Π·Π²Π΅ΡˆΠ΅Π½Π½Ρ‹Ρ… с ΡƒΡ‡Π΅Ρ‚ΠΎΠΌ ΠΈΡ… ΠΏΡ€ΠΎΠ΅ΠΊΡ‚ΠΈΠ²Π½ΠΎΠ³ΠΎ покрытия, Π΄Π°ΡŽΡ‚ Ρ„ΠΈΡ‚ΠΎΠΈΠ½Π΄ΠΈΠΊΠ°Ρ†ΠΈΠΎΠ½Π½ΡƒΡŽ ΠΎΡ†Π΅Π½ΠΊΡƒ экологичСского Ρ„Π°ΠΊΡ‚ΠΎΡ€Π°. ΠŸΡ€ΠΈ ΠΏΡ€ΠΈΠ±Π»ΠΈΠΆΠ΅Π½ΠΈΠΈ ΠΊ ΠΌΠ°Ρ€Π³ΠΈΠ½Π°Π»ΡŒΠ½Ρ‹ΠΌ позициям Π³Ρ€Π°Π΄ΠΈΠ΅Π½Ρ‚Π° происходит ΡƒΠ²Π΅Π»ΠΈΡ‡Π΅Π½ΠΈΠ΅ асиммСтричности распрСдСлСния Π²ΠΈΠ΄ΠΎΠ². Π’Π°ΠΊΠΎΠ΅ явлСниС Π½Π°Π±Π»ΡŽΠ΄Π°Π΅Ρ‚ΡΡ ΠΏΡ€ΠΈ исслСдовании Ρ€Π΅Π°Π»ΡŒΠ½Ρ‹Ρ… Π³Ρ€Π°Π΄ΠΈΠ΅Π½Ρ‚ΠΎΠ². Π­Ρ‚ΠΈ явлСния Ρ‚Π°ΠΊΠΆΠ΅ ΡΠ²Π»ΡΡŽΡ‚ΡΡ слСдствиСм матСматичСских свойств экологичСских шкал. Для модСлирования ΠΊΡ€ΠΈΠ²Ρ‹Ρ… ΠΎΡ‚ΠΊΠ»ΠΈΠΊΠ° распрСдСлСния Π²ΠΈΠ΄ΠΎΠ² Π² качСствС Π°Π»ΡŒΡ‚Π΅Ρ€Π½Π°Ρ‚ΠΈΠ²Ρ‹ симмСтричной гауссовой ΠΌΠΎΠ΄Π΅Π»ΠΈ примСняСтся Ξ²-функция. Π­Ρ‚Π° функция ΠΌΠΎΠΆΠ΅Ρ‚ ΠΌΠΎΠ΄Π΅Π»ΠΈΡ€ΠΎΠ²Π°Ρ‚ΡŒ ΠΊΠ°ΠΊ симмСтричныС, Ρ‚Π°ΠΊ ΠΈ асиммСтричныС распрСдСлСния. Π’Π°ΠΊ ΠΊΠ°ΠΊ фитоиндикация выполняСт ΠΎΠ±Ρ€Π°Ρ‚Π½ΡƒΡŽ Π·Π°Π΄Π°Ρ‡Ρƒ Π² сравнСнии с ΠΌΠΎΠ΄Π΅Π»ΠΈΡ€ΠΎΠ²Π°Π½ΠΈΠ΅ΠΌ ΠΊΡ€ΠΈΠ²Ρ‹Ρ… ΠΎΡ‚ΠΊΠ»ΠΈΠΊΠ°, Ρ‚ΠΎ Π²ΠΏΠΎΠ»Π½Π΅ умСстно Ξ²-Ρ„ΡƒΠ½ΠΊΡ†ΠΈΡŽ Ρ‚Π°ΠΊΠΆΠ΅ ΠΏΡ€ΠΈΠΌΠ΅Π½ΠΈΡ‚ΡŒ для Ρ€Π΅ΡˆΠ΅Π½ΠΈΡ Π·Π°Π΄Π°Ρ‡ Ρ„ΠΈΡ‚ΠΎΠΈΠ½Π΄ΠΈΠΊΠ°Ρ†ΠΈΠΈ. ΠŸΡ€ΠΈΠΌΠ΅Π½Π΅Π½ΠΈΠ΅ Ξ²-Ρ„ΡƒΠ½ΠΊΡ†ΠΈΠΈ ΠΏΠΎΠ·Π²ΠΎΠ»ΠΈΠ»ΠΎ ΠΎΡ†Π΅Π½ΠΈΡ‚ΡŒ Π·ΠΎΠ½Ρƒ ΠΎΠΏΡ‚ΠΈΠΌΡƒΠΌΠ° Π²ΠΈΠ΄Π° Π½Π° основС Π΅Π³ΠΎ ΠΊΠ°Ρ€Π΄ΠΈΠ½Π°Π»ΡŒΠ½Ρ‹Ρ… Ρ‚ΠΎΡ‡Π΅ΠΊ с ΡƒΡ‡Π΅Ρ‚ΠΎΠΌ вСроятной асиммСтрии распрСдСлСния ΠΊΡ€ΠΈΠ²ΠΎΠΉ ΠΎΡ‚ΠΊΠ»ΠΈΠΊΠ° Π²ΠΈΠ΄Π°. Π’Π°ΠΊΠΆΠ΅ ΠΌΠΎΠ΄Π΅Π»ΠΈΡ€ΠΎΠ²Π°Π½ΠΈΠ΅ ΠΊΡ€ΠΈΠ²ΠΎΠΉ распрСдСлСния Π²ΠΈΠ΄Π° Π΄Π°Π΅Ρ‚ Π²ΠΎΠ·ΠΌΠΎΠΆΠ½ΠΎΡΡ‚ΡŒ ΡΡƒΠ·ΠΈΡ‚ΡŒ Π΄ΠΈΠ°ΠΏΠ°Π·ΠΎΠ½ Π²ΠΎΠ·ΠΌΠΎΠΆΠ½Ρ‹Ρ… Π·Π½Π°Ρ‡Π΅Π½ΠΈΠΉ экологичСского Ρ„Π°ΠΊΡ‚ΠΎΡ€Π°, Π² условиях ΠΊΠΎΡ‚ΠΎΡ€ΠΎΠ³ΠΎ Π²ΠΈΠ΄ ΠΌΠΎΠΆΠ΅Ρ‚ Π΄Π΅ΠΌΠΎΠ½ΡΡ‚Ρ€ΠΈΡ€ΠΎΠ²Π°Ρ‚ΡŒ наблюдаСмоС ΠΎΠ±ΠΈΠ»ΠΈΠ΅ Π² сообщСствС. БоотвСтствСнно, это ΡƒΠ²Π΅Π»ΠΈΡ‡ΠΈΠ²Π°Π΅Ρ‚ ΠΈΠ½Ρ„ΠΎΡ€ΠΌΠ°Ρ†ΠΈΠΎΠ½Π½ΡƒΡŽ Ρ†Π΅Π½Π½ΠΎΡΡ‚ΡŒΒ Π²ΠΈΠ΄ΠΎΠ² Π² сообщСствС ΠΈ Ρ‚Π°ΠΊΠΈΠΌ ΠΎΠ±Ρ€Π°Π·ΠΎΠΌ ΠΏΠΎΠ·Π²ΠΎΠ»ΡΠ΅Ρ‚Β Π΄ΠΎΡΡ‚ΠΈΡ‡ΡŒ большСй надСТности Ρ„ΠΈΡ‚ΠΎΠΈΠ½Π΄ΠΈΠΊΠ°Ρ†ΠΈΠΎΠ½Π½Ρ‹Ρ… ΠΎΡ†Π΅Π½ΠΎΠΊ

    Intra-population spatial structure of the land snail Vallonia pulchella (MΓΌller, 1774) (Gastropoda; Pulmonata; Valloniidae)

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    ABSTRACT. This paper summarizes the mechanisms behind the patterning of the intra-population spatial arrangement of the land snail Vallonia pulchella in terms of edaphic and vegetation properties. The mol- luscs were collected from a regular grid in recultivated soil (the research station of Dnipro State Agrarian and Economic University, Pokrov, Ukraine). As predictors of the snail population abundance, spatial variables were used, as well as edaphic and vegetation indices. It is shown that V. pulchella prefers microsites character- ized by higher soil electrical conductivity, which con- tain larger aggregate fractions with low mechanical im- pedance and the low temperature at the depth of 0-10 cm, with a more developed dead plant layer, low-light and low hygromorph and heliomorph index values of the vegetation

    Recreation and terrain effect on the spatial variation of the apparent soil electrical conductivity in an urban park

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    Recreation is an important cultural ecosystem service and is able to significantly affect soil heterogeneity and vegetation func-tioning. This study investigated the role of the relief and tree stand density in the apparent soil electrical conductivity variation within an urban park. The most suitable variogram models were assessed to evaluate the autocorrelation of the regression models. The map of the spatial variability of apparent soil electrical conductivity was built on the basis of the most suitable variogram. The experimen-tal polygon was located in the Botanical Garden of Oles Honchar Dnipro National University (Dnipro City, Ukraine). The experi-mental polygon was formed by a quasi-regular grid of measurement locations located about 30 m apart. The measurements of the apparent electrical conductivity of the soil in situ were made in May 2018 at 163 points. On average, the value of soil apparent elec-tric conductivity within the investigated polygon was 0.55 dSm/m and varied within 0.17–1.10 dSm/m. Such environment predictors as tree stand density, relief altitude, topographic wetness index, and potential of relief to erosion were able to explain 48% of the observed variability of soil electrical conductivity. The relief altitude had the greatest influence on the variation of soil electrical con-ductivity, which was indicated with the highest values of beta regression coefficients. The most important trend of the electric con-ductivity variation was due to the influence of relief altitude and this dependence was nonlinear. The smallest values of the soil elec-trical conductivity were recorded in the highest and in lowest relief positions, and the largest values were detected in the relief slope. Recreational load can also be explained by the geomorphology predictors and tree stand density data. These predictors can explain 32% of the variation of recreational load. The variogram was built both for the soil apparent electrical conductivity dataset and for the residuals of the regression model. As a result of the procedure of the models’ selection on the basis of the AIC we obtained the best estimation of the variogram models parameters for the electrical conductivity and for the regression residuals of the electrical conduc-ti vity. The level of recreation was correlated statistically significantly with the apparent soil electrical conductivity. The residuals of regression models in which geomorphological indicators and tree stand density were used as predictors have a higher correlation level than the original variables. The soil electrical conductivity may be a sensitive indicator of the recreation loa
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