Article

Scale and Species Richness: Towards a General, Hierarchical Theory of Species Diversity

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Aim Current weaknesses of diversity theory include: a failure to distinguish different biogeographical response variables under the general heading of diversity; and a general failure of ecological theory to deal adequately with geographical scale. Our aim is to articulate the case for a top-down approach to theory building, in which scale is addressed explicitly and in which different response variables are clearly distinguished. Location The article draws upon both theoretical contributions and empirical analyses from all latitudes, focusing on terrestrial ecosystems and with some bias towards (woody) plants. Methods We review current diversity theory and terminology in relation to scale of applicability. As a starting point in developing a general theory, we take the issue of geographical gradients in species richness as a main theme and evaluate the extent to which commonly cited theories are likely to operate at scales from the macro down to the local. Results A degree of confusion surrounds the use of the terms alpha, beta and gamma diversity, and the terms local, landscape and macro-scale are preferred here as a more intuitive framework. The distinction between inventory and differentiation diversity is highlighted as important as, in terms of scale of analysis, are the concepts of focus and extent. The importance of holding area constant in analysis is stressed, as is the notion that different environmental factors exhibit measurable heterogeneity at different scales. Evaluation of several of the most common diversity theories put forward for the grand clines in species richness, indicates that they can be collapsed to dynamic hypotheses based on climate or historical explanations. The importance of the many ecological/biological mechanisms that have been proposed is evident mainly at local scales of analysis, whilst at the macro-scale they are dependent largely upon climatic controls for their operation. Local communities have often been found not to be saturated, i.e. to be non-equilibrial. This is argued, perhaps counter-intuitively, to be entirely compatible with the persistence through time of macro-scale patterns of richness that are climatically determined. The review also incorporates recent developments in macroecology, Rapoport's rule, trade-offs, and the importance of isolation, landscape impedance and geometric constraints on richness (the mid-domain effect) in generating richness patterns; highlighting those phenomena that are contributory to the first-order climatic pattern, and those, such as the geometric constraints, that may confound or obscure these patterns. Main conclusions A general theory of diversity must necessarily cover many disparate phenomena, at various scales of analysis, and cannot therefore be expressed in a simple formula, but individual elements of this general theory may be. In particular, it appears possible to capture in a dynamic climate-based model and `capacity rule', the form of the grand cline in richness of woody plants at the macro-scale. This provides a starting point for a top-down, global-to-local, macro-to-micro scale approach to modelling richness variations in a variety of taxa. Patterns in differentiation/endemicity, on the other hand, require more immediate attention to historical events, and to features of geography such as isolation. Thus, whilst we argue that there are basic physical principles and laws underlying certain diversity phenomena (e.g. macro-scale richness gradients), a pluralistic body of theory is required that incorporates dynamic and historical explanation, and which bridges equilibrial and nonequilibrial concepts and ideas.

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... One of the most important challenges facing ecologists and biogeographers is to understand patterns of spatial and temporal variations in species richness and diversity (MacArthur, 1972;Lomolino, 2001). Latitudinal gradients in species richness and diversity, and the species-area relationships are among the most discussed and documented of these (Rahbek, 1997;Whittaker et al ., 2001;Willig et al ., 2003). Richness and diversity patterns on elevation gradients are, however, little understood, and have only been documented recently (Rahbek, 1995(Rahbek, , 1997Wang et al ., 2002;Bhattarai & Vetaas, 2003), calling into doubt the hypothesis that species richness and diversity decrease monotonically with increasing elevation. ...
... Both the correlation and the regression tree analyses showed significant associations between species richness and diversity and elevation. Elevation gradients basically reflect precipitation and temperature gradients (Pavón et al ., 2000;Whittaker et al ., 2001;Wang et al ., 2002). The observed unimodal species richness pattern suggests that it could have resulted from the influence of local physical variables (i.e. ...
... Grime (1979) and Huston and DeAngelis (1994) found species richness to be lower where resources were lowest, it was high at intermediate levels, and decreased gradually as resource levels were higher. This pattern is not universal; the specific group of variables responsible for variations in species richness and diversity may be complex and may differ significantly between ecosystems and in different spatial an temporal scales (Pausas & Austin, 2001;Whittaker et al ., 2001). It is also difficult to distinguish the local effects of physical and chemical soil characteristics on species richness and diversity, due to their dynamic, interactive nature. ...
Article
This article presents an analysis of plant species richness and diversity and its association with climatic and soil variables along a 1300-m elevation gradient on the Cerro Tláloc Mountain in the northern Sierra Nevada in Mexico. Two 1000-m2 tree sampling plots were created at each of 21 selected sampling sites, as well as two 250-m2 plots for shrubs and six 9-m2 plots for herbaceous plants. Species richness and diversity were estimated for each plant life form, and beta diversity between sites was estimated along the gradient. The relationship between species richness and diversity and environmental variables was modelled using simple linear correlation and regression trees. Species richness and diversity showed a unimodal pattern with a bias towards high values in the lower half of the elevation gradient under study. This response was consistent for all three life forms. Beta diversity increased steadily along the elevation gradient, being lower between contiguous sites at intermediate elevations and high – the species replacement rate was nearly 100%– between sites at the extremes of the gradient. Few species were adapted to the full spectrum of environmental variation along the elevation gradient studied. The regression tree suggests that differences in species richness are mainly influenced by elevation (temperature and humidity) and soil variables, namely A2 permanent wilting point, organic matter and horizon field capacity and A1 horizon Mg2+.
... Conversely, between-site floristic dissimilarity (beta diversity) allows the evaluation of each community's ecological uniqueness relative to the regional diversity and the complementarity between sites (Vellend 2001;Legendre and Cáceres 2013). Understanding how the combination of alpha and beta diversity originates patterns of regional (gamma) diversity has become a crucial strategy for setting up priorities for biodiversity conservation (Whittaker et al. 2001;Tuomisto 2010). Such a multilevel approach enables assessing the importance of each site for the regional species pool and floristic diversity maintenance across large landscapes (Lande 1996;Whittaker et al. 2001;Felfili and Felfili 2001). ...
... Understanding how the combination of alpha and beta diversity originates patterns of regional (gamma) diversity has become a crucial strategy for setting up priorities for biodiversity conservation (Whittaker et al. 2001;Tuomisto 2010). Such a multilevel approach enables assessing the importance of each site for the regional species pool and floristic diversity maintenance across large landscapes (Lande 1996;Whittaker et al. 2001;Felfili and Felfili 2001). ...
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Transitional vegetation zones in the neotropics harbor high biodiversity and are threatened by advancing deforestation and climate change. Besides, the diversity patterns at multiple spatial scales are little understood. We investigated the woody flora of eight savanna sites over 700 km along the transition zone between the Cerrado and Amazonia. We assessed plant diversity at three spatial scales: alpha (α = local richness), beta (βJac = Jaccard mean dissimilarity of species composition between sites), and gamma (γ = regional diversity). We also measured the sites’ contribution to beta diversity (LCBD) to unveil the ecological singularity of the transition. We found high local richness (α = ∼80 species per hectare) and high between-site dissimilarity (βJac = 0.651; LCBD = 0.354), which together contributed to high regional diversity (γ = 167). There was no relationship between floristic composition and proximity between sites or proximity to Amazonia. The locally dominant species (representing 80% or more of the total abundance) also differed across sites, indicating the unique composition of each community. This high floristic diversity at different spatial scales is severely threatened by extensive deforestation in recent decades and a paucity of protected areas, stressing the need for protected areas and conservation actions.
... L'étude des gradients environnementaux du SSL sur les composantes biologiques relève une hétérogénéité mesurable à différentes échelles spatiales (Laprise et Dodson, 1993;Whittaker et al., 2001;Frenette et al., 2006;Frenette et al., 2012;Roy et al., 2014). Par conséquent, pour comprendre les processus influençant les composantes biologiques du SSL, il importe de prendre en considération la localisation des sites d'échantillonnage et l'aire à l'étude dans son ensemble (Whittaker et al., 2001;Roy et al., 2014). ...
... L'étude des gradients environnementaux du SSL sur les composantes biologiques relève une hétérogénéité mesurable à différentes échelles spatiales (Laprise et Dodson, 1993;Whittaker et al., 2001;Frenette et al., 2006;Frenette et al., 2012;Roy et al., 2014). Par conséquent, pour comprendre les processus influençant les composantes biologiques du SSL, il importe de prendre en considération la localisation des sites d'échantillonnage et l'aire à l'étude dans son ensemble (Whittaker et al., 2001;Roy et al., 2014). À ce jour, H2. ...
Research
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Les organismes benthiques jouent des rôles importants dans les écosystèmes aquatiques tels que l'oxygénation, la décomposition ou le recyclage de la matière organique. Toutefois, les pressions environnementales et anthropiques croissantes menacent le bon fonctionnement de ces systèmes et engendrent une baisse de la diversité benthique, qui mériteraient d'être mieux documentées. Le Saint-Laurent, considéré comme l'un des plus grands systèmes hydrographiques au monde, présente une mosaïque d'habitats variés, de forts gradients environnementaux et de nombreuses pressions humaines, tous susceptibles d'influencer les communautés benthiques à divers degrés. Cette étude s'est intéressée à trois régions hydrologiques du Saint-Laurent : la portion fluviale, l'estuaire fluvial et l'estuaire moyen. L'objectif était de caractériser la composition et la répartition des différentes communautés benthiques dans une portion contrastée du système Saint-Laurent et d'identifier les variables environnementales qui expliquaient le mieux leur présence. Les communautés benthiques ont été échantillonnées à 113 stations de Montréal à Cacouna de 2018 à 2020. Les embranchements Annelida et Arthropoda étaient les deux taxons les plus représentés dans notre échantillonnage. Les analyses de groupement ont révélé neuf communautés benthiques influencées par les gradients environnementaux propres des régions hydrologiques. Les masses d'eau, la salinité, la nature des sédiments ainsi que la température étaient les quatre variables clés qui expliquaient 16 % de la relation entre les communautés et les variables environnementales. Cette étude a mis en évidence les effets de processus régionaux sur la structure des communautés benthiques et suggère l'implication de plusieurs effets locaux. Enfin, c'est la première fois qu'une étude portant sur les communautés benthiques couvre à la fois le fleuve et l'estuaire du Saint-Laurent. Ce travail à grande échelle permet d'affiner la compréhension de l'écosystème et contribue à améliorer la pertinence des indicateurs benthiques.
... The number of distinct species found in a sample was our measure of richness [35]. Evenness, as determined by the Pielou index, is the degree to which the abundance of various species is uniform or similar. ...
... We also applied the inverse Simpson index, which is an indicator of richness in a community with the same evenness, and the Shannon index, which takes into account the number of species living in a habitat (richness) and their relative abundance (evenness). Beta diversity refers to the difference in diversity between individuals [35]. ...
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A comprehensive understanding of gut microbiota in a clearly defined group of healthy individuals is essential when making meaningful comparisons with various diseases. The Mediterranean diet (MD), renowned for its potential health benefits, and the influence of adherence thereto on gut microbiota have become a focus of research. Our aim was to elucidate the impact of adherence to the MD on gut microbiota composition in a well-defined cohort. In this prospective study, healthy volunteers completed a questionnaire to provide demographic data, medical history, and dietary intake. Adherence was evaluated using the Med-DQI. The V4 region of the 16S rRNA gene was sequenced. Analysis of sequencing data and statistical analysis were performed using MOTHUR software and R. The study included 60 patients (51.7% females). Adherence correlated with alpha diversity, and higher values were recorded in good adherers. Good adherers had a higher abundance of Paraprevotella and Bacteroides (p < 0.001). Alpha diversity correlated inversely with fat intake and positively with non-starch polysaccharides (NSPs). Evenness correlated inversely with red meat intake and positively with NSPs. Predicted functional analysis highlighted metabolic pathway differences based on adherence to the MD. In conclusion, our study adds useful information on the relationship between the MD and the gut microbiome.
... Most importantly, the species category is of paramount importance for biogeographical research. Aggregating locality records for species distribution modelling (Pearson et al., 2006), calculating species richness (Field et al., 2009;Whittaker et al., 2001), or comparing patterns of biodiversity across islands (Triantis et al., 2012), all rely on current species-level taxonomy. In fact, 22 of the top-50 JBI papers (https:// onlin elibr ary. ...
... While the advent of phylogenomics and population genomics has facilitated the detection of ever-shallower phylogeographical units within species, with the associated risk of taxonomic inflation, at the same time, a tremendous number of species remain undiscovered and unnamed. They are thus inaccessible for global and regional biogeographical analyses which uncover general macroecological rules (Field et al., 2009;Freeman & Pennell, 2021;Triantis et al., 2012;Whittaker et al., 2001), and set global conservation priorities in the face of global change (e.g., Albuquerque & Beier, 2015;Diniz-Filho et al., 2013;Jenkins et al., 2013;McQuatters-Gollop et al., 2017;Pacifici et al., 2015;Sigwart, 2018). ...
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An accurate species-level taxonomy is paramount for biogeographical research, and conversely, biogeographical data are of importance for species delimitation. We here review recent developments and future perspectives of taxonomy of direct relevance for biogeographers. The understanding that species are independently evolving segments of population-level lineages, the rise of integrative approaches to delimit such lineages, and the advent of high-throughput sequencing have considerably renewed the discipline of taxonomy. Using genome-scale molecular datasets, the extent of admixture across hybrid zones can now be effectively assessed and the evolutionary independence of lineages inferred, leading to more reliable and comparable species delimitation criteria. Substantially divergent but admixing phylogeographical lineages can conveniently be named as subspecies, thus avoiding taxonomic oversplitting and taxonomic inflation. At the same time, comprehensive DNA barcoding and DNA metabarcoding efforts are uncovering an enormous proportion of undiscovered biotic diversity, and we encourage the development of bioinformatic pipelines that combine high-throughput species discovery and delimitation with diagnosis and scientific naming, to approach a biotic inventory of the globe without abandoning the established Linnaean system.
... Given the scale-dependent nature of biodiversity , Spake et al., 2021, it is crucial for studies examining diversity patterns and drivers to account for scale. Indeed, patterns and drivers of species richness can be influenced by spatial grain, i.e. the measurement unit or area within which species occurrences are quantified (Whittaker et al., 2001). Species richness is the count of species per unit area, and therefore, the choice of grain size may affect the species richness measured (Bhatta et al., 2018). ...
... Thus, in environmentally heterogeneous landscapes, which often exhibit higher beta diversity, there is a notable advantage to adopt a multi-scale approach to understand biotic and abiotic factors shaping species richness. For instance, the productivity-species richness relationship is notably affected by sampling grain size (Whittaker et al., 2001). Coarse grains exhibit a monotonically positive relationship, whereas finer grains show a hump-shaped pattern, with maximum species richness at intermediate productivity (Virtanen et al., 2013). ...
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Environmental and biotic factors drive species richness patterns, but the nature of this relationship can vary with sampling grain. Understanding the scale-dependent effects of these factors is crucial for interpreting species richness patterns in ecosystems experiencing rapid environmental change. We investigated the effects of local environmental drivers on plant species richness at small (1 x 1 m) and large (3 x 3 m) sampling grains, and the factors correlated with differences in richness between the two grains, on a sub-Antarctic island. Broadly, richness was higher in warmer (i.e., lower altitude, north-facing) and wetter (i.e., higher topographic wetness index, lower distance from drainage line) sites, and in more topographically heterogenous (i.e., steeper slopes) sites. Additionally, there was some evidence of competition with a keystone plant limiting species richness, though this was only evident at low elevations. However, the effects of several drivers on richness depended on spatial grain. Differences in species richness between large and small grain sizes were more pronounced at low elevations, indicating that there is more compositional heterogeneity at low altitudes at both grains. Richness was positively related to northness at large grain size but not at small grain size, suggesting that higher northness increases local turnover at a grain size > 1 m2. On the other hand, TWI boosted richness at small but not large grains, implying that competition limited coexistence at low TWI, and that higher TWI only resulted in more species coexisting at a grain of 1 m2, while having no effect on richness at large grains. Our study therefore highlights that drivers of plant species richness can vary with sampling grain, suggesting that environmental effects on local species turnover affect richness patterns at different grains. Assessing how the influence of such drivers differ with grain size provides insight into local patterns of species assemblage.
... De manera general, las hipótesis propuestas para esclarecer el fenómeno de distribución de especies en cuanto la latitud y altitud son varias e involucran a factores como la heterogeneidad espacial, el tiempo, la competencia y depredación, estabilidad climática y la productividad del sitio (Painka, 1966;Whittaker et al., 2001;Sanders et al., 2007), el tiempo evolutivo, tiempo ecológico, la estructura del hábitat, (Scheibe, 1987), la relación agua-energía (Fu et al., 2006), la relación espacial o relación especies-área (Brown y Lomolino, 1998) entre otras. ...
... Patterns of biodiversity are not constant and are highly variable, both on spatial and temporal scales [3]. Many studies have shown high levels of variance on large spatial scales; however, measurable differences in biodiversity do occur on small spatial scales [4,5]. Ecotones are regions of transition in which one ecosystem coincides with another [6][7][8]. ...
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Introduction: Biodiversity is not static, and regions with high levels of temporal and spatial variation or ecotones, may be critical for maintaining high biodiversity. The micro-tidal zone or transition from marine to terrestrial environments is a region with high levels of temporal and spatial variation. Ophiuroidea and Echinoidea have physiological and behavioural adaptions which allow them to be abundant in the micro-tidal zone. There is little research on the diversity of Ophiuroidea and Echinoidea on small spatial and temporal scales within the micro-tidal zone. Methods: This study aims to determine the possibility of a micro-tidal zone acting as an ecotone through analysis of Ophiuroidea and Echinoidea spatial and temporal diversity. Ecological Data was collected along two transects in the micro-tidal zone of Half Moon Caye, Belize. Shannon diversity indices were calculated and used for conditional probabilities to assess biodiversity at various regions in the zone. Statistical analysis was done with the Kruskal-Wallis Test, linear regression, and Chi-square analysis. Results: Evidence suggests that A. punctulata differs from all other species in the distance from high tide, this corresponds to the high conditional probability close to shore compared to other species. A relationship was found between the distance from high tide and both abundance and species richness. O. appressa and E. lucunter abundance was determined to be dependent of the time of day, but this was independent for all other species. Discussion: Patterns in biodiversity suggest that the outer region of the micro-tidal zone has a higher species richness due to overlap with species adapted to deeper locations. Furthermore, there is evidence which suggests there may be differences throughout shallower portions of the micro-tidal zone, but further analysis needs to be done with consideration of the physical conditions in this region. In addition to spatial differences, there were differences seen depending on the time of day which may suggest that some species move out of the intertidal zone at night. Conclusion: This study indicates how the tropical micro-tidal zone may be a critical region acting as an ecotone, providing habitat for a wide range of species on different spatial and temporal scales.
... Hillside forest tree richness was negatively correlated with the annual temperature variation. This result supports the hypothesis of environmental variability, which suggests that fewer species can tolerate variable environmental conditions, leading to a decline from the tropics to temperate zones (Whittaker et al. 2001;Ruggiero and Kitzberger 2004). The effect of climate variability or seasonality on species richness has been less studied than the absolute effect of variables such as temperature. ...
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Background The Rio de la Plata grassland region is dominated by temperate grasslands, with the scarce natural forests, influenced floristically by adjacent biogeographical provinces. Uruguay represents the southern limit for many tree species of the Paranaense Province, several of which inhabit the hillside forests. With many species shifting poleward due to climate change, we do not yet know how current environmental factors, particularly climatic ones, are linked to the tree diversity of this flora nowadays. The aim of this study is to understand the geographic pattern of tree richness in the hillside forests of Uruguay, evaluating the water–energy and the environmental heterogeneity hypotheses. The distribution of the hillside forest trees was obtained by compiling and updating the herbaria database and distribution maps of woody plants of Uruguay. The presence/absence of each species, and then the species richness, were georeferenced over a grid that covers Uruguay with 302 cells (660 km ² ). Over the same grid were compiled environmental variables associated with climate and environmental heterogeneity. The relationship between richness and environmental variables was studied by applying general linear models (GLM). As a strong autocorrelation was detected, a residuals auto-covariate term was incorporated into the GLM, to take into account the species richness spatial structure. Results The tree flora of the hillside forest was composed mainly by Paranaense species that show a latitudinal gradient, with two high richness cores, in the east and northeast of Uruguay. The final model including the environmental variables and the spatial term explained 84% of the variability of tree richness. Species richness showed a positive relationship with precipitation, forest cover, potential evapotranspiration and productivity, while a negative effect of temperature variation was found. The spatial component was the primary predictor, accounting for a 30% of spatial pattern of tree richness. Conclusions This study accounts for a large proportion of the environmental and spatial variations of the tree richness pattern of the Paranense flora in its southernmost portion. It brings support to both water–energy and environmental heterogeneity hypotheses, emphasizing the role of climate and its variation and the habitat availability on the hillside forest diversity.
... To the best of our knowledge, causal relationships between phylogenetic and taxonomic diversity in vascular plants have not been found at the alpha level (Hurtado et al., 2019;Loṕez-Angulo et al., 2020). The possible reason is that beta diversity, which explicitly considers the species identity of community composition compared to alpha diversity, provides a more sensitive indicator of biotic changes caused by human disturbance (Whittaker et al., 2001). Regardless, the result suggests that environmental changes possibly select species of particular clades from the regional lineage pool, with species retention or exclusion according to the adaptive potential to particular environmental constraints. ...
Article
As an increasingly prevalent form of human activity, roads drive the taxonomic homogenization of mountain plant assemblages, threatening global biodiversity. However, little is known about how mountain roads impact functional and phylogenetic beta diversity and how these effects are related to taxonomic homogenization. To understand the mechanism of taxonomic homogenization triggered by mountain roads, we used species absence/ presence data from 76 plots (2 m*50 m) and values for 12 traits measured on 978 species from the interior and roadside communities in the Qionglai mountain range, one of the temperate regions with the highest plant species richness in the world. We used a structural equation modeling approach (SEM) to consider several surrogates of road disturbance (changes in soil physicochemical properties and the presence or absence of roads) and the causal relationship between three facets of beta diversity (taxonomic beta diversity, TBD; functional beta diversity, FBD and phylogenetic beta diversity, PBD). The results suggest that TBD, FBD and PBD respond inconsistently to mountain roads, despite strong positive correlations between the three facets of plant beta diversity in the study area. Compared with the interior community, the btotal.tax and btotal.func of the roadside community decreased by 2.54% and 2.22%, respectively, which were related to the reduction of species and trait richness differences and replacements; however, we did not find the same results when assessing the changes in btotal.phy, which represents tip-weighted PBD (twPBD). Furthermore, the largest effect of roads on beta diversity was reflected in basal-weighted PBD (bwPBD), which decreased by 9.97%, indicating that those species with fewer extant relatives and longer evolutionary histories are more sensitive to mountain roads. Therefore, it is necessary to take targeted protection measures for ancient species in roadside communities. In addition, we believe that it is still necessary to take measures to Frontiers in Plant Science Understanding the taxonomic homogenization of road-influenced plant assemblages in the Qionglai mountain range: A functional and phylogenetic perspective. prevent the further dispersal of nonnative species, although the presence of non-native species in roadside plots has led to small changes in three facets of beta diversity. There were causal relationships between the three facets of beta diversity, but their intensity and sign different in the SEM of different components of beta diversity (i.e., richness difference and replacement). Our findings suggest that the homogenization of community species composition at the landscape scale arises by a combination of adaptive responses of the functional traits of organisms to environmental consistency (e.g., reduced the differences in soil variables) caused by roads and resorting or reassembly of community clades composition due to environmental filtering. These results contribute to our comprehensive understanding of the impact of mountain roads on plant diversity, which highlights the complex relationship between human pressure and biodiversity loss.
... Studies on animal communities, including ant communities (Cushman & McGarigal, 2002;Whittaker et al., 2001), have identified a hierarchical suite of factors affecting diversity and community composition, including large-scale biogeographic factors like primary productivity down to small-scale environmental heterogeneity and soil characteristics (Maravalhas & Vasconcelos, 2020;Pérez-S anchez et al., 2023;Spiesman & Cumming, 2008). Within this range of scales, vegetation or land use type can vary across landscapes, whereas vegetation cover or complexity can vary at much smaller, local scales (Oliver et al., 2016;Spiesman & Cumming, 2008). ...
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Habitat structure is a key determinant of local animal diversity, with attributes of vegetation such as cover or complexity generating key resources for different species. However, habitat–diversity relationships can vary across spatial scales, and among different taxa and ecosystem types. Here we report on a study of habitat structure and its effects on ant communities at two spatial scales in a temperate grassy woodland characterized by heterogenous tree and grassland cover. We examined species richness and the occurrence of ground‐dwelling ant species at (1) microhabitat scales defined by a triplet of sites comprising open ground, adjacent to a log, and under a tree, each separated by a few meters, and (2) at macrohabitat scales defined by sites grouped into broader vegetation types defined by low or high levels of shrub and tree cover and separated by 100s of meters. We identified 117 species of ant from 41 genera, from a total of 155,004 individuals collected. Ant community composition differed significantly among microhabitats and macrohabitats, but mean species richness only differed at the microhabitat scale where it was the highest under trees and lower adjacent to logs and in open ground. Notably, ant species within the genera Iridomyrmex , Monomorium , and Pheidole displayed a spectrum of microhabitat preferences, highlighting the ecological flexibility within these groups. By contrast, all species of Melophorus preferred open habitat and all species of Camponotus preferred habitat under trees. Our study shows that ant communities in grassy woodlands are structured by vegetation cover and habitat “openness” most strongly at “microhabitat” scales, which is likely due to a distinct combination of thermal and foraging attributes that vary across relatively small distances. Our results also suggest that broad classifications of ants into functional types based on vegetation preference may not be applicable at small scales where species within the same genus can display contrasting preferences. Land management that promotes habitat heterogeneity at small spatial scales may promote species coexistence and benefit ant diversity more than management activities focusing on larger spatial scales within the same ecosystem.
... Thus the speciesenergy relationship (the relationship between energy availability and species richness) may clarify this pattern between species richness and elevation. Receiving a specified content of energy can preserve a specified number of species which means higher elevations shelter fewer species than lowlands (Gaston, 2000;Whittaker et al., 2001;Willis and Whittaker, 2002;Aubry et al., 2005). The lower diversity in higher elevations implies that the species inhabiting these areas face fewer competitors. ...
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Introduction Land snails play a crucial role in maintaining ecosystem sustainability within their habitats. Therefore, understanding the characteristics of their communities is vital for ecological studies and the development of effective conservation strategies. In this study, land snail communities inhabiting the Hyrcanian forest were identified and the variations in their community composition along elevational gradients were investigated. Methods Snail samples were collected from three distinct elevations in three different forest locations within the Hyrcanian area of Iran. This study utilized DNA barcoding to identify land snail species. By employing statistical analyses such as ANOVA and PERMANOVA, significant differences in the features of snail communities across different elevations were examined. Concurrently, soil samples were collected from each site to assess soil physicochemical parameters about snail presence. Result Through this comprehensive analysis, a total of 10 OTUs, were further classified into seven families, and nine genera were identified. Five of these genera had never been reported in the study region before. We observed a decline in OTU richness with increasing elevation; however, the maximum abundance of snails was found at higher elevations. CCA demonstrated that Ca, Mg, and moisture saturation predominantly shape snail community composition. Discussion The unique climatic conditions and spatial distribution of precipitation from lowlands to highlands, as well as from west to east, make the Hyrcanian forests an ideal case study area for understanding the dynamics of land snail communities. In summary, this study provides new insights into the land snail communities thriving in the Hyrcanian forests. The findings from our research can contribute to the development of effective conservation management strategies for forest ecosystems. By understanding the factors influencing the distribution and composition of land snail communities, we can make informed decisions to protect and preserve land snails and the balance they maintain within their habitats.
... Community assembly at multiple spatial scales has been an essential topic in community ecology 20 (Fukami and Morin, 2003). Assessments of how species diversity is distributed has become 21 relevant due to provision of ecosystem services (Tscharntke et al., 2012;Whittaker et al., 2001). that our small mammal assemblage data span several years of sampling (from 1986 to 2015) and 109 that land use has changed substantially over time, we tried to obtain the most accurate 110 information by extracting land use data for the average years of sampling. ...
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Understanding how the mammalian diversity responds to anthropogenic disturbances on local and landscape scales is an urgent task. The Atlantic Forest biome, with only 12% of its original area remaining, still harbors great diversity of small mammals (Rodentia and Didelphimorphia), a key group that responds quickly to disturbances. Here, using the largest dataset of Atlantic Forest small mammals, we evaluate how forest amount and bioclimatic variables affect the non-volant small mammal diversity. For this purpose, we use 214 small mammal assemblages across the Atlantic Forest domain. Our results show that forest amount, with a positive relation, was the most important predictor explaining the diversity of small mammals in Atlantic Forest remnants. We also found that the bioclimatic variables (temperature and precipitation) can positively and/or negatively affect small mammal biodiversity, depending on the region analyzed. This is the first study that has assessed diversity across the entire Atlantic Forest biome, showing the importance of large-scale assessment and of forest amount and bioclimatic variables in shaping the diversity of small mammals regardless of the biogeographic context.
... Conversely, during economic growth, asset correlations might decrease as investors diversify their portfolios to exploit various opportunities (Baele et al. 2020). Similarly, in ecological systems, the dynamics governing species populations and environmental variables reveal intricate temporal correlations operating at multiple time scales (Whittaker, Willis, and Field 2001). In Figure 1, we provide an example where, in time scale 1 , we can observe a positive correlation between two time series, whereas in the shorter scale 2 , we might notice a negative correlation between them. ...
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Multivariate time series forecasting poses an ongoing challenge across various disciplines. Time series data often exhibit diverse intra-series and inter-series correlations, contributing to intricate and interwoven dependencies that have been the focus of numerous studies. Nevertheless, a significant research gap remains in comprehending the varying inter-series correlations across different time scales among multiple time series, an area that has received limited attention in the literature. To bridge this gap, this paper introduces MSGNet, an advanced deep learning model designed to capture the varying inter-series correlations across multiple time scales using frequency domain analysis and adaptive graph convolution. By leveraging frequency domain analysis, MSGNet effectively extracts salient periodic patterns and decomposes the time series into distinct time scales. The model incorporates a self-attention mechanism to capture intra-series dependencies, while introducing an adaptive mixhop graph convolution layer to autonomously learn diverse inter-series correlations within each time scale. Extensive experiments are conducted on several real-world datasets to showcase the effectiveness of MSGNet. Furthermore, MSGNet possesses the ability to automatically learn explainable multi-scale inter-series correlations, exhibiting strong generalization capabilities even when applied to out-of-distribution samples.
... Biodiversity can be evaluated across scales by evaluating alpha, beta, and gamma diversity (70). Alpha diversity refers to species richness, which is the number of species within a community. ...
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Understanding deep-time marine biodiversity change under the combined effects of climate and connectivity changes is fundamental for predicting the impacts of modern climate change in semi-enclosed seas. We quantify the Late Miocene–Early Pliocene (11.63–3.6 Ma) taxonomic diversity of the Mediterranean Sea for calcareous nannoplankton, dinocysts, foraminifera, ostracods, corals, molluscs, bryozoans, echinoids, fishes, and marine mammals. During this time, marine biota was affected by global climate cooling and the restriction of the Mediterranean’s connection to the Atlantic Ocean that peaked with the Messinian Salinity Crisis. Although the net change in species richness from the Tortonian to the Zanclean varies by group, species turnover is greater than 30% in all cases. The results show clear perturbation already in the pre-evaporitic Messinian (7.25–5.97 Ma), with patterns differing among groups and sub-basins.
... Exploring the drivers of biodiversity across environmental and spatial gradients is at the core of community ecology, macroecology, landscape ecology, and conservation (Rosenzweig 1995, Whittaker et al. 2001, McGill et al. 2007, Heino et al. 2015, Chase et al. 2020, Banks-Leite et al. 2022). These drivers operate at local scales, e.g. ...
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IInfluential ecological research in the 1980s, elucidating that local biodiversity (LB) is a function of local ecological factors and the size of the regional species pool (γ-diversity), has prompted numerous investigations on the local and regional origins of LB. These investigations, however, have been mostly limited to single scales and target groups and centered exclusively on γ-diversity. Here we developed a unifying framework including scale, environmental factors (heterogeneity and ambient levels), and metacommunity properties (intraspecific spatial aggregation, regional evenness, and γ-diversity) as hierarchical predictors of LB. We tested this framework with variance partitioning and structural equation modeling using subcontinental data on stream diatoms, insects, and fish as well as local physicochemistry, climate, and land use. Pure aggregation + regional evenness outperformed pure γ-diversity in explaining LB across groups. The covariance of the environment with aggregation + regional evenness rather than with γ-diversity generally explained a much greater proportion of the variance in diatom and insect LB, especially at smaller scales. Thus, disregarding aggregation and regional evenness, as commonly done, may lead to gross underestimation of the metacommunity effects and the indirect environmental effects on LB. We examined the shape of the local-regional species richness relationship, which has been widely used to infer local vs. regional effects on LB. We showed that this shape has an ecological basis, but its interpretation is not straightforward. Therefore, we advocate that the variance partitioning analysis under the proposed framework is adopted instead. In diatoms, metacommunity properties had the greatest total effects on LB, while in insects and fish, it was the environment, suggesting that larger organisms are more strongly controlled by the environment. Broader use of our framework may lead to novel biogeographical insights into the drivers of LB and improved projections of its trends along current and future environmental gradients.
... Elevation and abiotic factors are the governing drivers for differences in species richness and composition in the Himalaya (Lee and Chun, 2016;Pandey et al., 2018a). The species composition depends directly on temperature and air pressure, which decrease along the elevation gradient (Whittaker et al., 2001;Bhattarai and Vetaas, 2006;. It is well established that diversity declines linearly along the elevation gradient (MacArthur, 1972;Korner, 2000). ...
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The present study describes how vegetation (the tree layer) is shaped along the elevation gradients in the eastern part of the Indian Himalayan Region. Various vegetation attributes, distribution, population structure, and regeneration patterns of 75 tree species belonging to 31 families were studied. Tree species richness shows a low plateau (peaked between 1,300-1,500 m) with a linearly decreasing pattern above 1,500 m asl. Ericaceae was found as the dominant family, followed by Lauraceae and Rosaceae. The distributional pattern of species-to-genera ratio (S/G) did not follow any particular trends, while β-diversity increased along the elevation gradient. The Margalef index of species richness, the Menheink index of species richness, and the Fisher alpha were found to be highest at lower altitudes (1,000-1,500 m), while the Simpson index was highest at middle altitudes (2,600-3,000 m). Random distribution was shown by maximum tree species (47.3%), followed by a contagious distribution (42.9%), and regular distribution (10.8%). The regeneration of tree species was found to be good with a healthier number of seedlings (10.2%), fair (43.5%), poor (30.3%), while 16% were observed not regenerating. Acer laevigatum (1,500 m), Prunus nepalensis (3,300 m), Viburnum sympodiale (3,400 m) were among the new regenerating species at the respective altitudes. The population structure of tree species in terms of proportion of individuals in seedlings, saplings, and the adult class varied in all the elevation transects. Species with better regeneration on upper distribution limits have been recognized as probable for upward movement.
... Elevation and abiotic factors are the governing drivers for differences in species richness and composition in the Himalaya (Lee and Chun, 2016;Pandey et al., 2018a). The species composition depends directly on temperature and air pressure, which decrease along the elevation gradient (Whittaker et al., 2001;Bhattarai and Vetaas, 2006;. It is well established that diversity declines linearly along the elevation gradient (MacArthur, 1972;Korner, 2000). ...
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The present study describes how vegetation (the tree layer) is shaped along the elevation gradients in the eastern part of the Indian Himalayan Region. Various vegetation attributes, distribution, population structure, and regeneration patterns of 75 tree species belonging to 31 families were studied. Tree species richness shows a low plateau (peaked between 1,300–1,500 m) with a linearly decreasing pattern above 1,500 m asl. Ericaceae was found as the dominant family, followed by Lauraceae and Rosaceae. The distributional pattern of species-to-genera ratio (S/G) did not follow any particular trends, while β-diversity increased along the elevation gradient. The Margalef index of species richness, the Menheink index of species richness, and the Fisher alpha were found to be highest at lower altitudes (1,000–1,500 m), while the Simpson index was highest at middle altitudes (2,600– 3,000 m). Random distribution was shown by maximum tree species (47.3%), followed by a contagious distribution (42.9%), and regular distribution (10.8%). The regeneration of tree species was found to be good with a healthier number of seedlings (10.2%), fair (43.5%), poor (30.3%), while 16% were observed not regenerating. Acer laevigatum (1,500 m), Prunus nepalensis (3,300 m), Viburnum sympodiale (3,400 m) were among the new regenerating species at the respective altitudes. The population structure of tree species in terms of proportion of individuals in seedlings, saplings, and the adult class varied in all the elevation transects. Species with better regeneration on upper distribution limits have been recognized as probable for upward movement.
... This pattern is contrary to the results of species richness found in primary forests in the same area of SBR by Torres et al. [7] in the Ecuadorian Amazon, as well as in a protected primary forest in the Tumbesian dry forest ecoregion [46], where the number of tree species increased with increasing altitude. This variation trend in primary forests may be due to the fact that species distribution patterns are the result of multiple ecological processes [47], influenced by geographic differences and environmental factors such as climate and soil [48], but on the other hand, the evidence of decreasing species richness with increasing altitude in anthropic systems, such as the dispersed trees in these pasture systems, could be the result of the establishment and management of production systems generated by populations of mestizo settlers who came at different times and with different cultural backgrounds and used the ecosystem for different purposes, according to Torres et al. [10]. The first livestock settlements in the SBR occurred in the Amazon highland zone about 70 years ago, then in the lower zone about 45 years ago and, finally, in the middle zone about 35 years ago, which is in agreement with Lei and Zhouping's reports [49] that suggest different stages of succession showed different species composition in natural pastures studied in China. ...
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This study analyzes tree diversity and its ecological importance value in silvopastoral systems in the Sumaco Biosphere Reserve (SBR), Ecuador, along an altitudinal gradient of 400-2000 masl. Twenty-six plots distributed into low (400-700 masl), medium (701-1600 masl) and high (1601-2000 masl) zones were used. The Shannon index and the importance value index (IVI), based on abundance, dominance and relative frequency, were estimated. The results highlight that in pastures with dispersed trees, the richness of trees decreases with increasing altitude in the elevational gradient; they also show a higher tree density at lower altitudes in contrast to the Andean-Amazonian primary forests. The lower and middle zones showed higher diversity, linked to regeneration and the presence of nearby forests. Species of high commercial value, such as Cedrela odorata and Jacaranda copaia, were common, reflecting knowledge of the local timber market. In the lower and middle zones, the 10 most important species accounted for more than 70% of the trees, with up to 96% in the upper zone. A total of 51 taxa (including 42 species and nine taxa at the rank of genus) were identified, which were mostly native; 64.7% are classified by the IUCN as least-concern (LC) species, 31.4% as not evaluated (NE) species and 3.9% as vulnerable (VU) species, specifically highlighting Cedrela odorata and Cedrela montana. The study concludes with policy recommendations related to the importance of trees in silvopastoral systems for the conservation of species and the livelihoods of local communities, highlighting the need for responsible management of Amazonian pasturelands.
... This size unit would align with the type of conservation investments made at a landscape to regional scale. Our results are in line with the expectation that topography and soil play a substantial role in biodiversity patterns at this scale [57]. The CNS surrogate strategy we have evaluated here, could help inform conservation agendas targeting increased representation within ecoregions [33] and initiatives that are not continent-wide but follow arbitrary political boundaries [21,58]. ...
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Conserving Nature's Stage (CNS) is a concept from conservation planning that promotes the protection of areas encompassing a broad range of enduring geophysical traits to provide long-term habitat for diverse species. The efficacy of using enduring geophysical characteristics as surrogates for biodiversity, independent of non-geophysical features and when considering finer resolution area selections, has yet to be investigated. Here, we evaluated CNS using 33 fine-scale inventories of vascular plant, non-vascular plant, invertebrate or vertebrate species from 13 areas across three continents. For each inventory, we estimated a continuous multidimensional surrogate defined from topographic and soil estimates of the surveyed plots. We assessed surrogate effectiveness by comparing the species representation of surrogate selected plots to the representation from plots picked randomly and using species information. We then used correlation coefficients to assess the link between the performance and qualities of the inventories, surroundings and surrogates. The CNS surrogate showed positive performance for 24 of the 33 inventories, and among these tests, represented 28 more species than random and 83&percnt; of the total number of species on average. We also found a small number of weak correlations between performance and environmental variability, as well as qualities of the surrogate. Our study demonstrates that prioritizing areas for a variety of geophysical characteristics will, in most cases, promote the representation of species. Our findings also point to areas for future research that might enhance CNS surrogacy. This article is part of the Theo Murphy meeting issue ‘Geodiversity for science and society’.
... In each transect, we also quantified proportion of vegetation types such as grasses (gramineous plants), herbs (shorter plants with soft stems), trees, halophytic shrubs (shrubs adapted to grow in environments with high levels of salt), other shrubs with woody stems >1 m, and subshrubs (shrubs <1 m) from 100 observations spaced at 50 cm per transect. We measured vegetation diversity in each transect as the number of species or taxa and the distribution of individuals or indices weighted by abundance distributions of species (Whittaker et al. 2001). To estimate vegetation diversity, we considered the proportion of vegetation types and calculated a modified Shannon diversity index, exp H ( ) Sh or exp (Shannon), which is the exponential of Shannon entropy . ...
Article
Environmental heterogeneity shapes the traits of natural populations, including space use and burrowing behavior. We studied the red viscacha rat ( Tympanoctomys barrerae ), a semifossorial rodent with patchy distribution in drylands of west‐central Argentina, to provide ecological data on habitat and burrow features of this specialist species. We collected data on 165 burrows and 55 individuals from 2017–2018 and observed correlations between different vegetation types, vegetation diversity, and physical attributes (e.g., soil hardness). A high number of individual red viscacha rats was negatively associated with herbs. The number of burrow entrances was positively associated with harder soils and negatively associated with vegetation cover. Our results suggest that the species' patchy distribution is strongly associated with environmental heterogeneity of these arid environments, and consequently provide an essential step towards conserving their populations across their geographic range.
... The following indices were used to assess the plant communities (Magurran, 1998;Whittaker et al., 2001): ...
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Introduction Tajikistan is a typical mountainous country covered by different mountain grasslands that are important pasture resources. Recently, grassland degradation has become widespread due to climate change and human activities and fertilization has been used to improve grassland production. However, fertilizer inputs can substantially alter species diversity, but it is uncl\ear how productivity and species diversity respond to nutrient enrichment in the mountain meadows of Tajikistan. Methods Therefore, a 5-year (2018–2022) continuous in-situ mineral fertilizer experiment was conducted to examine the effects of three nitrogen (N) levels (0, 30, and 90 kg N ha–1 year–1), two phosphorus (P) levels (0 and 30 kg P ha–1 year–1), and their combinations on above-ground biomass (AGB) and species diversity in a mountain meadow grassland in Ziddi, Varzob region, Tajikistan. Five species diversity metrics—Margalef’s species richness (Dma), the Shannon–Wiener index (H), the Simpson index (C), Pielou’s equitability index (Epi), and the Evar Species Evenness index (Evar)—were used to measure species diversity. Results and discussions The results indicated that the addition of different N and P amounts and their various combinations considerably increased both total and dominant species AGB, with the highest increase occurring in the N90P30 (90 kg N ha–1 year–1 combined with 30 kg P ha–1 year–1) treatment in 2022; during the experiment, the importance value of Prangos pabularia (dominant species) first decreased and then increased, but its dominant status did not change or fluctuate among the years. Furthermore, N, P, and their different combinations had no significant effect on species diversity (Dma, H, C, Epi, and Evar). All the species diversity indexes fluctuated among years, but there was no interaction with mineral fertilizer addition. Total AGB had a negative relationship with species diversity and low concentration N fertilizer addition (N30; P30) strengthened this negative trend. However, this trend decreased under the high N fertilizer condition (N90P30). Overall, nutrient addition to the natural mountain grassland of the Varzob region improved AGB, which meant that there was more forage for local animals. Mineral fertilizers had no significant effect on species diversity, but may enhance P. pabularia dominance in the future, which will help maintain the stability of the plant community and improve the quality of the forage because P. pabularia is an excellent and important winter fodder. Our study suggests that scientific nutrient management could effectively promote grassland production, conserve plant variety, and regenerate degraded grassland, which will counteract the desertification process in northwest Tajikistan mountain meadows.
... Such losses can have a negative impact on phylogenetic diversity when related species become extinct (Santos et al. 2010;Andrade et al. 2015;Silva-Junior et al. 2018). While most studies have focused on local (α) diversity to assess biodiversity loss in human-modified landscapes (Whittaker et al. 2001), it is important to recognize that local diversity represents only a fraction of the regional diversity. The impact of such new landscapes on the spatial dissimilarities of the remaining biota (β-diversity) remains poorly understood, particularly in the tropics (Karp et al. 2012). ...
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Changes caused by anthropogenic disturbances are a major driver of local diversity, but their effects on the species replacement across space (β-diversity), remain poorly understood, particularly with respect to different life-stages and ecological groups. We investigated these effects by examining juvenile and adult assemblages of shade-tolerant and intolerant tree species in 20 Brazilian Atlantic Forest fragments. We quantified taxonomic and phylogenetic β-diversity among forest fragments and assess landscape predictors that might explain species turnover. Additionally, we assessed the turnover between juvenile and adult assemblages within forest fragments. Our results show that taxonomic β-diversity among forest fragments was higher in adults than juvenile assemblages, mainly to shade-intolerant species, indicating a time lag between life-stages. In contrast, phylogenetic β-diversity among forest fragments was consistently low and similar between life-stages and ecological groups (shade-tolerant and intolerant species). Forest cover and geographic distance were the main drivers of taxonomic β-diversity, while edge amount was not an important predictor. Within each forest fragment, we reveal a high taxonomic turnover among life-stages, characterized by a broad shift between juvenile and adult assemblages, irrespective of forest cover. Conversely, phylogenetic turnover was influenced by forest cover, exhibiting a greater dissimilarity among life-stages in deforested landscapes. These findings underscore the importance of considering different life-stages to capture temporal responses between juveniles and adults, as well as to anticipate future community dynamics. Forest loss appears to drive taxonomic homogenization, by influencing changes in species composition. This results in a future juvenile community that is more similar among fragments than the current community. Additionally, forest loss induces phylogenetic changes within fragments, ultimately leading to future communities with different composition and evolutionary heritage compared to natural forested landscapes.
... Multiple studies have focused on the role of green areas in promoting high levels of biodiversity in cities (e.g., Alvey 2006;Bonthoux et al. 2014;Hui et al. 2017). For instance, the main UNF attributes that regulate biodiversity include habitat heterogeneity, mediated by different types of forest species and/or habitats (Kang et al. 2015); patch size, considering the largest patches as more diverse habitats (e.g., Whittaker et al. 2001;Godefroid and Koedam 2003); and forest connectivity between natural areas, which allows for greater genetic flow, benefiting the fauna inhabiting these forests (e.g., Pardini et al. 2005;Faria 2009). Thus, an urban forest with high habitat heterogeneity, large patches, and higher connectivity with natural forests should contain high species diversity and abundance. ...
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Here, we explore the suitability of a temperate UNF for saproxylic beetles. These beetles are deadwood-dependent, highly diverse trophic groups that commonly inhabit natural forest ecosystems. However, saproxylic beetle diversity has been understudied in urban forest ecosystems. We analyzed the species richness, abundance, and seasonal variation of saproxylic beetles, including their most important trophic guilds, associated with urban forests. For this purpose, we monitored standing dead trees monthly between December 2019 and December 2022, using trunk window (flight interception) traps in the UNF Arboretum of Valdivia, Chile. Additionally, we measured qualitative and quantitative habitat attributes to evaluate the preferences of these insects in the UNF. We used generalized linear models as statistical methods to estimate saproxylic beetle habitat preferences. We collected 1273 individuals, belonging to 43 families and 195 saproxylic species/morphospecies. We found that diversity and abundance were strongly influenced by seasonality and the degree of decomposition of deadwood, with increased diversity and abundance in warmer months and highly decomposed trees. Our data show that UNF Arboretum harbor a high diversity of saproxylic species and are therefore suitable habitats and that the factors that regulate these assemblages are homologous to those of natural forests. Finally, our research provides evidence useful for the establishment of conservation and management practices to promote high diversity in UNFs, for example increasing the deadwood volume and quality of the habitat for saproxylic diversity.
... These differences are highly significant (p < 0.01) and show a decrease in species and family diversity with increasing altitude. This variation may be due to the fact that species distribution patterns are the result of multiple ecological processes [38], influenced by geographic differences and environmental factors such as climate and soil [39], but on the other hand, the dispersed trees in these pasture systems could be 5 established and managed by populations of mestizo settlers who came at different times and with different cultural backgrounds and different inheritance of the ecosystem, according to Torres et al. [40]. The first livestock settlements in the SBR occurred in the Amazon highland zone about 70 years ago, then in the lower zone about 45 years ago, and finally in the middle zone about 35 years ago, which is in agreement with Lei and Zhouping reports [41], that different stages of succession showed different species composition in natural pastures studied in China. ...
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This study analyzes tree diversity and its ecological importance value in silvopastoral systems in the Sumaco Biosphere Reserve (SBR), Ecuador, along an altitudinal gradient of 400-2000 masl. Twenty-six plots distributed in low (400-700 masl), medium (701-1600 masl) and high (1601-2000 masl) zones were used. The Shannon index and the Importance Value Index (IVI), based on abundance, dominance and relative frequency, were estimated. The results show variations in the diameter structure of the trees, influenced by factors such as settlement history and pasture management. The lower and middle zones showed higher tree density and diversity, linked to regeneration and the presence of nearby forests. Species of high commercial value, such as Cedrela odorata and Jacaranda copaia, were common, reflecting knowledge of the local timber market. In the lower and middle zones, the 10 most important species accounted for more than 70% of the trees, and up to 96% in the upper zone, indicating the need for further research on abundance factors and promotion of diversification in pastures. A total of 51 tree species were identified, mostly native, 64.7% are classified by the IUCN as "Least Concern", 31.4% as "Not Evaluated", and 3.9% as "Vulnerable", specifically highlighting Cedrela odorata and Cedrela Montana. The study concludes with policy recommendations related to the importance of trees in silvopastoral systems for the conservation of species and the livelihoods of local communities, highlighting the need for responsible management of Amazonian pasturelands.
... It has been argued that biotic interactions are less influential in shaping species distributions at larger scales and secondary to the abiotic factors at the range level (Soberon, 2007;Soberón & Nakamura, 2009;Whittaker et al., 2001). Recent work instead suggests that biotic interactions, together with abiotic factors, are important in shaping patterns of species' distribution and cooccurrence, and including these interactions would improve species distribution models (Anderson, 2017;Anderson et al., 2002;Araujo & Rozenfeld, 2014;De Araújo et al., 2014;Dormann et al., 2018;Engelhardt et al., 2020;Gherghel et al., 2018;Jenkins et al., 2020;Mod et al., 2015). ...
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Aim The evolutionary interactions between western spadefoot toads (genus Spea ) represent a textbook example of character displacement, facilitated by dietary specialization of one Spea species on fairy shrimp (Anostraca) when all three co‐occur. The aim of this study is to understand the covariation between predator ( Spea ) and prey (Anostraca) range shifts in response to climate change oscillations, and whether biotic interactions can be used to project species distribution models on different time scales when studying species with dietary specialization. Taxon: Amphibia: Spea spp. and Crustacea: Anostraca. Location North America. Methods Using multiple modelling techniques, we first estimated the potential distribution of central and western North American fairy shrimp species (Crustacea: Anostraca) and two western spadefoot toad species ( Spea bombifrons and Spea multiplicata ). We then created a shrimp species richness map by aggregating individual species estimates. Third, we studied the relationship between the probability of spadefoot toad presence and fairy shrimp species richness during the present and Last Glacial Maximum conditions. Finally, we estimated the strength and direction of the co‐occurrence between spadefoot toads and fairy shrimp sampled at the level of entire predicted range and at the regional level (allopatric and sympatric). Results First, the same abiotic environmental variables shape spadefoot toad and fairy shrimp species' distributions in central and western North America across time. Second, areas of sympatry of Spea bombifrons and Spea multiplicata correspond with dry conditions and higher shrimp richness. Finally, the spatial patterns of predator–prey co‐occurrence are highly variable across geography, forming a spatial mosaic over the species' ranges. Main Conclusion Predator–prey relationships form a spatial mosaic across geography and species ranges. Including biotic interactions into species distribution estimates for organisms with dietary specialization is highly recommended. Biotic interactions can be projected across different time frames for organisms with dietary specialization as they are likely conserved.
... Environmental effects on rocky intertidal assemblages varied across spatial scales, supporting the scale dependence of environmental drivers of species richness (Whittaker et al., 2001;Willis & Whittaker, 2002). Environmental factors showed nonsignificant relationships with macroalgal and polychaete diversity at the latitudinal scale. ...
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Latitudinal biodiversity gradients vary across taxonomic groups and spatial scales, and various environmental factors have been associated with those patterns. However, it remains unknown whether taxonomic groups with strong ecological associations have similar or different latitudinal patterns. Macroalgae are foundation assemblages on rocky intertidal shores and are often inhabited by invertebrates, predominantly polychaetes. This study analysed latitudinal patterns of macroalgae and their associated polychaetes at different spatial scales and determined how environmental factors influenced those patterns. Macroalgae and polychaetes were collected from transects within 38 rocky intertidal shores of Western Australia at 14 latitudes between 18° S and 34° S. Latitudinal gradients in species richness, diversity (Simpson's diversity index) and abundance were evaluated at transect, site and latitudinal scales. Relationships between environmental factors and rocky intertidal assemblages were analysed using piecewise structural equation modelling based on direct, indirect and complex models. Macroalgae showed increases in species richness, diversity and abundance at transect and site scales towards high latitudes, but species richness and diversity patterns were unclear at the latitudinal scale where transect and site data were pooled. In contrast, polychaete diversity decreased towards high latitudes, although this pattern was unclear at the transect scale. Polychaete richness and abundance tended to follow parabolic patterns that peaked at 27° S. Relationships between environmental factors and rocky intertidal assemblages were best described by a complex model, with significant relationships more often at transect and site scales. Sea surface temperatures showed the strongest relationship with macroalgal and polychaete distributions.
... The role of competition in particular has been a classic (Pianka 1981) and controversial issue (Wiens 2011, Fraterrigo et al. 2014 as it is identified rather rarely and idiosyncratically across studies and taxa. Other assembly processes such as dispersal and environmental filtering are frequently addressed in macroecological approaches; however, the coarse resolution and poor sampling representativeness of those (Gotelli et al. 2010, Barnagaud et al. 2021) impede inferences on biotic interactions, as biotic effects likely define ecological patterns at finer spatial scales (Whittaker et al. 2001, Willis andWhittaker 2002). Fortunately, the recent increasing availability of high-resolution occurrence data promises an unprecedented potential for general understanding of assembly processes across large spatial scales. ...
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Our understanding of how biotic interactions influence animal community assembly is largely restricted to local systems due to the difficulty of obtaining ecologically meaningful assemblage data across large spatial extents. Here, we used thousands of spatio‐phenologically high‐resolution assemblages across three distinct European regions together with a functional diversity approach to understand community assembly of dragonflies and damselflies (Odonata), an insect group characterized by a pronounced competitive reproductive biology. We found that adult dragonfly, but not damselfly, assemblages were consistently composed of species morphologically more different than expected by chance based on the traits that enhance their interspecific reproductive encounters. These results provide consistent evidence for the role of competition in the assembly of animal communities, which we interpret is most likely caused by the territorial reproductive biology of dragonflies. Support for competition varied both spatially and seasonally following theoretical expectations, as it was strongest in locations and seasonal moments with low thermal stress (i.e. warm conditions) and high niche packing. Our study illustrates how spatio‐temporal diversity patterns arise from variation in assembly processes.
... To make matters more complex still, the generalisability of setting thresholds and baselines across biodiversity facets and taxonomic groups is not a given. Macroecological concepts are almost always discussed within the context of a system, area or taxon; pluralistic theories of macroecological phenomena are preferred over simplified explanations (Whittaker et al., 2001). For example, novelty in aquatic systems could also be expected to respond and propagate differently to terrestrial counterparts. ...
Article
The concept of novel ecosystems has been discussed for over more than a decade to describe ecosystems that have an altered species composition and function, such that the community has crossed a threshold forbidding a return to its historical state. While spatial and temporal community compositional change has been well studied in biogeography, studies on novel ecosystems in a modern context are few and tend towards classifying novelty based on a static baseline. Given that the abiotic and biotic drivers of novelty are in a state of rapid change, and reaching levels unprecedented within the last hundred thousand to million years, defining such a threshold requires additional thought. Here, we discuss a biogeographical–macroecological perspective on novel ecosystems, exploring how such a threshold for novelty can be defined in an environment undergoing progressive global change and suggesting pathways through which the emergence and spread of novelty can be further explored, understood and managed.
... The controversial observations of importance of factors may be an artifact of the scale of study, since it is fundamental in ecology to determine how we perceive patterns and processes, and therefore affects our ability to explain and predict (Ricklefs Robert E., 1987;Wiens, 1989) When concerning species richness at local scales (∼10²-10³ km²) systems, species richness within communities is more influenced by fine-scale abiotic and biotic interactions and habitat structure disturbances, such as fires and storms (Whittaker et al., 2001). At a landscape level (~10³ km²), soil type and altitude are more likely to influence species turnover (Clarke & Lidgard, 2000). ...
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Effect of spatial scale in biotic and abiotic factors in the distribution of the chytrid fungus in the Atlantic Forest Efeito da escala espacial em fatores bióticos e abióticos na distribuição do fungo quitrídeo na Mata Atlântica CAMPINAS 2020
... Habitat productivity, climate, soil properties, and spatial scale may influence the relationship between species richness and grazing intensity (Baaker et al., 2006;Gao & Carmel, 2020a, 2020bLezama et al., 2014;Milchunas et al., 1988;Olff & Ritchie, 1998;Whittaker et al., 2001). Moderate intensities of grazing may result in greater species richness in subhumid grasslands but not in dry environments (Milchunas et al., 1988). ...
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Plant species richness is an important property of ecosystems that is altered by grazing. In a semiarid environment, we tested the hypotheses that (1) small‐scale herbaceous plant species richness declines linearly with increasing grazing intensity by large ungulates, (2) precipitation and percent sand interact with grazing intensity, and (3) response of herbaceous plant species richness to increasing intensity of ungulate grazing varies with patch productivity. During January–March 2012, we randomly allocated 50, 1.5‐m × 1.5‐m grazing exclosures within each of six 2500 ha study sites across South Texas, USA. We counted the number of herbaceous plant species and harvested vegetation in 0.25‐m ² plots within exclosures (ungrazed control plots) and in the grazed area outside the exclosures (grazed treatment plots) during October–November 2012–2019. We estimated percent use (grazing intensity) based on the difference in herbaceous plant standing crop between control plots and treatment plots. We selected the negative binomial regression model that best explained the relationship between grazing intensity and herbaceous plant species richness using the Schwarz‐Bayesian information criterion. After accounting for the positive effect of precipitation and percent sand on herbaceous plant species richness, species richness/0.25 m ² increased slightly from 0% to 30% grazing intensity and then declined with increasing grazing intensity. Linear and quadratic responses of herbaceous plant species richness to increasing grazing intensity were greater for the least productive patches (<15.7 g/0.25 m ² ) than for productive patches (≥15.7 g/0.25 m ² ). Our results followed the pattern predicted by the intermediate disturbance hypothesis model for the effect of grazing intensity on small‐scale herbaceous plant species richness.
... A fundamental pattern of great interest to ecologists is how and why species diversity changes with location or time. Species diversity is scale dependent [1,2] and, as such, is generally examined with regards to three spatial levels: alpha (α)-, beta (β)-, and gamma Insects 2023, 14, 847 2 of 12 (γ)-diversity [3][4][5]. Alpha diversity is the number of species in a local assemblage, whereas γ-diversity is the number of species in a regional pool. The change in species composition among local assemblages within a region is β-diversity. ...
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Simple Summary Biodiversity is measured differently depending on the spatial scale of the study. Beta (β)-diversity, for example, is a calculated measurement that addresses changes in diversity across different assemblages in a specific region. Studies of β-diversity often address changes in diversity across gradients of environmental conditions and distance among sites. However, β-diversity of stream insects can be difficult to measure due to their hyper-diversity and challenging taxonomy. Our study investigated the association of β-diversity with habitat conditions and distance among these habitats for insects found in the coastal streams of Alabama, USA. Additionally, we looked for potential influences caused by seasonality (fall and summer) and the level of taxonomic identification (genus, species). Regardless of season, stream conditions were highly correlated with β-diversity. More specifically, stream size and water chemistry showed the highest associations with β-diversity. Changes in β-diversity were largely driven by species replacement (turnover) rather than species loss (nestedness). The taxonomic resolution had minimal effects on the calculations of β-diversity across environmental conditions. Distance among stream sites was never correlated with β-diversity. As we continue to face global insect declines, our study provides valuable insight into the patterns that drive changes in diversity across environmental gradients. Abstract β-diversity is often measured over both spatial and temporal gradients of elevation, latitude, and environmental conditions. It is of particular interest to ecologists, as it provides opportunities to test and infer potential causal mechanisms determining local species assemblages. However, studies of invertebrate β-diversity, especially aquatic insects, have lagged far behind other biota. Using partial Mantel tests, we explored the associations between β-diversity of insects found in the coastal streams of Alabama, USA, and stream conditions and distances among sites. β-diversity was expressed using the Sørensen index, βSor, stream conditions were expressed as principal components (PCs), and distances as Euclidean distances (km) among sites. We also investigated the impact of seasonality (fall, summer) and taxonomic resolution (genus, species) on βSor. Regardless of season, βSor was significantly correlated (p < 0.01; r > 0.44) with stream conditions (stream size and water chemistry), while taxonomic resolution had minimal effect on associations between βSor and stream conditions. Distance was never correlated with changes in βSor (p > 0.05). We extended the use of the Sørensen pair-wise index to a multiple-site dissimilarity, βMult, which was partitioned into patterns of spatial turnover (βTurn) and nestedness (βNest). Changes in βMult were driven mostly by turnover rather than nestedness.
... It is applied to combinations of local ecological communities up to the scale of entire biomes, continents, and ocean basins. Thus, a megadiverse region can either have high species richness within each of the occurring habitats (alpha) or high diversity of different habitats and niches within the landscape mosaic (beta) or both (Whittaker et al. 2001;Lomolino et al. 2017). The scale dependence applies not only to species richness patterns, but also to explanatory environmental variables. ...
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Biodiversity is in sharp decline at many scales, declining faster than at any time in human history. On the other hand, it is of inestimable value for humans and their well-being since it safeguards ecosystem functioning and secures the provisioning of ecosystem services on which human civilization is utterly dependent. The global distribution of biodiversity is highly uneven. Striking contrasts are to be observed between the incredible diversity of tropical plants and animals and the much less diverse floras and faunas in temperate regions and higher latitudes. Evolution, speciation, immigration, extinction, and ecological interactions are fundamental processes underlying the latitudinal gradient of species richness. Recent global assessments of the status and trends of biodiversity and ecosystem services consistently showed that in the wake of the ‘Great Acceleration’ the rate of decline of biodiversity has increased dramatically. Around 1 million species currently face extinction. The current global rate of species extinction is at its highest level in 65 million years and at least tens to hundreds times higher than it has averaged over the past 10 million years. Thus, we find ourselves in the sixth mass extinction in the history of the Earth. Population declines, species extinctions and the associated erosion of ecosystem services are systemic problems in the Anthropocene to be attributed to direct drivers, with changes in land and sea use, direct exploitation of resources, climate change, pollution, and invasion of alien species having the largest global impact. These direct drivers are again linked to indirect drivers related to developments in economy, politics and society. Since none of the global biodiversity conservation targets has been achieved to date, urgent and concerted efforts are needed to enable transformative change in lifestyles and economies over the long term in order to maintain and restore the fabric of life that supports us all.
... Community stability and species diversity vary widely among successional stages, and the stability of a community directly responds to the current successional state of the community [6]. Species diversity and richness are the core of ensuring stability [7]. At present, there are three possible relationships between species diversity and stability: positive, negative, and correlated, which have not been uniformly understood. ...
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... In ecology, biological diversity expresses the variety within an ecosystem and is characterized by two parameters, namely "richness", which is the number of different species in the same sample, and "evenness", which measures the relative abundance of individual species within the same ecosystem [27,28]. In the context of the ongoing debate concerning the oncogenic role of single versus multiple infections, the objective of the present study is the analysis of whether the richness of HPV genotype infections and the biodiversity of cervical dysplasias may play a significant role in determining the progression of precancerous lesions. ...
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The impact of multiple infections on the risk of cervical lesions is a subject of ongoing debate. This study aims to explore whether the richness of HPV genotype infections and the biodiversity of squamous and glandular cervical dysplasias could influence the progression of precancerous lesions. We conducted a cross-sectional analysis involving 469 women who attended the Colposcopy Unit at the European Institute of Oncology in Milan, Italy, from December 2006 to December 2014. HPV type richness was measured as the number of different genotypes per patient. We calculated the associations between richness and age, as well as histologic grade, along with Simpson’s biodiversity index for cervical dysplasias. We observed significant inverse relationships between the richness of high-risk (HR) genotypes and both age (p = 0.007) and histologic grade (p < 0.001). Furthermore, as the histologic grade increased, the mean biodiversity index of cervical dysplasias decreased, with exceptions noted in cases of normal histology and adenocarcinoma in situ. Different histologic grades formed five clusters with distinct mean ages and mean biodiversity indices. These findings suggest that HPV genotype richness and the biodiversity of cervical dysplasias may play a crucial role in predicting the risk of high-grade cervical lesions, enabling personalized management of precancers.
... Multiple studies have focused on the role of green areas in promoting high levels of biodiversity in cities (e.g., Alvey, 2006;Bonthoux et al., 2014;Hui et al., 2017). For instance, the main UNF attributes that regulate biodiversity include habitat heterogeneity, mediated by different types of forest species and/or habitats (Kang et al. 2015); patch size, considering the largest patches as more diverse habitats (e.g., Whittaker et al. 2001; Godefroid and Koedam 2003); and forest connectivity between natural areas, which allows for greater genetic ow, bene ting the fauna inhabiting these forests (e.g., Pardini et al. 2005;Faria 2006). Thus, an urban forest with high habitat heterogeneity, large patches, and higher connectivity with natural forests should contain high species diversity and abundance. ...
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Urban expansion is an important cause of biodiversity loss due to habitat destruction involving the replacement of the natural environment with anthropic infrastructure. However, recent studies suggest that the harmonious growth of cities could allow the persistence of biological diversity within them. Thus, some cities, especially those that contain remnant forests that preceded their expansion, could harbor high levels of biodiversity. These remnant forests, i.e., urban natural forests (UNFs), are refuges for native species, providing suitable habitat conditions for population stability. However, traditional ecological studies have focused on natural and planted forests, so our knowledge of ecological dynamics in UNFs is still limited. Here, we explore the suitability of a temperate UNF for saproxylic beetles. These beetles are deadwood-dependent, highly diverse trophic groups that commonly inhabit natural forest ecosystems. However, saproxylic beetle diversity has been understudied in urban forest ecosystems. We analyzed the species richness, abundance, and seasonal variation of saproxylic beetles, including their most important trophic guilds, associated with urban forests. For this purpose, we monitored standing dead trees monthly between December 2019 and December 2022, using trunk window (ight interception) traps. Additionally, we measured qualitative and quantitative habitat attributes to evaluate the preferences of these insects in the UNF. We used generalized linear models as statistical methods to estimate saproxylic beetle habitat preferences. We collected 1273 individuals, belonging to 43 families and 195 saproxylic species/morphospecies. We found that diversity and abundance were strongly in uenced by seasonality and the degree of decomposition of deadwood, with increased diversity and abundance in warmer months and highly decomposed trees. Our data show that UNFs harbor a high diversity of saproxylic species and are therefore suitable habitats and that the factors that regulate these assemblages are homologous to those of natural forests. Finally, our research provides evidence useful for the establishment of conservation and management practices to promote high diversity in UNFs, for example increasing the amount and quality of deadwood.
... Climate has been one of the main predictors of biodiversity because it determines levels of primary productivity and plant evapotranspiration, which in turn trigger cascading effects that affect the functioning of entire ecosystems, by determining cycles of matter and energy (Whittaker et al. 2001). Climate gradients and clines have gained importance in the literature focusing on the effects of past or future climate change on biodiversity, but here we focused on current climate (annual and seasonal temperature and precipitation) predicting patterns on horse fly diversity and endemism. ...
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With anthropogenic changes altering the environment and the subsequent decline of natural habitats, it can be challenging to predict essential habitats for elusive and difficult to study taxa. Primary burrowing crayfish are one such group due to the complexity in sampling their semi-terrestrial, subterranean habitat. Sampling burrows usually requires a labor-intensive, time-consuming excavation or trapping process. However, limited information on burrowing crayfish suggests that fine-scale habitat variation may drive burrowing crayfish habitat choice. This project aimed to evaluate the fine-scale habitat characteristics that influence burrowing crayfish presence and abundance at a large, restored-remnant grassland preserve in north-central Illinois. We documented burrow abundance and quadrat-specific habitat variables such as root biomass, canopy cover, apparent seasonal high-water table (water table) depth and dominant vegetation at sites with and without burrowing crayfish populations. Data was recorded at every quadrat and analyzed using generalized linear mixed models. A total of 21 models were created to determine what habitat variables affected burrow presence and abundance. We found that the water table depth was a significant driver of burrow presence and abundance. Root biomass and vegetation cover were not significant drivers, although they did show up in the final models, explaining the data. These findings demonstrate empirical support for previous observations from other burrowing crayfish research and demonstrate the influence of fine-scale habitat when modeling elusive taxa requirements.
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Since Xylella fastidiosa first appeared in southern Italy, it has become essential to manage and limit its transmission. In areas unaffected by the bacterium, such as Albania, it is necessary to assess the risk of its spread, primarily by understanding the ecology of its potential vectors. A survey of 14 olive orchards was conducted over a period of 12 months from August 2015 and July 2016 in two Albanian counties (Vlora and Tirana) where olive production is important. The aim was to investigate the presence of Auchenorrhyncha species, with particular attention to xylem feeders, and Auchenorrhyncha species belonging to the families Aphrophoridae, Cercopidae, Cicadellidae, Issidae, Flatidae were found in both counties. In Vlora, four out of 11 collected species were Aphrophoridae and Cercopidae, whereas in Tirana, three species belonging to these families were captured. In both counties, the most abundant xylem feeder species was Philaenus spumarius. In Vlora, P. spumarius was found more frequently on olive trees than in Tirana. Philaenus spumarius and Neophilaenus campestris adults were most frequent in August, September, and October 2015, while both species were almost absent from December 2015 to March 2016. Our sampling demonstrated that Vlora region has a greater number of Auchenorrhyncha species than Tirana. Furthermore, molecular tests (real-time LAMP) showed the absence of X. fastidiosa in the tested individuals. This survey constitutes an important update on the X. fastidiosa situation in Albania, showing that the country is still free of X. fastidiosa, at least in the surveyed areas.
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Background and aims – Endemism may be defined according to the time of origin of taxa. Neo-endemics refer to relatively recent species that have not dispersed outside their ancestral areas. In contrast, paleo-endemics refer to species of ancient origins, which are currently geographically restricted but probably were more widespread in the past. Geographically, endemism areas may also be based on the co-occurrence of more than one species. We aimed to qualitatively identify the neo-endemism and paleo-endemism of endemic Cactaceae of the Tehuacán-Cuicatlán Valley, as well as to quantitatively assess paleo- and neo-endemics areas. Material and methods – Using a dated molecular phylogeny of endemic Cactaceae, we defined paleo- and neo-endemics using an arbitrary boundary of 2.6 million years ago; we also assessed the significance of concentrations of these species using a categorical analysis of paleo- and neo-endemism. Key results – Our results showed that most endemic Cactaceae in the Tehuacán-Cuicatlán Valley arose throughout the Pleistocene, while categorical analysis indicated localised mixed- and super-endemism (including both paleo- and neo-endemics) areas. Conclusion – We suggest that paleo- and neo-endemics, as well as localised mixed-endemism areas, may have originated due to a probable high climatic stability in the Tehuacán-Cuicatlán Valley, which in addition to topographically rugged and ecologically complex zones (e.g. ecotones, isolated habitat patches) may have allowed it to function as a refuge throughout Pleistocene climatic changes, mainly promoting the speciation of neo-endemics, as well as the persistence of relatively few paleo-endemics.
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Following the overall discussion on conceptual and methodological issues, it is essential to start thinking about how to get data to evaluate patterns and processes in macroecology. We describe primary biodiversity data, gridding systems, and scale issues. We then show how such data can be organized and synthesized using a matrix approach in which species are the variables (descriptors) of the different spatial units (grid cells, for instance) covering a given domain (the matrix M). In general, this matrix is a binary, presence-absence matrix. Summing across columns estimates species richness, whereas summing across rows estimates the geographic range size for each species. These two emerging variables can be paired with spatial predictors at the cell level (e.g., environmental characteristics, geographical coordinates) and cross-species data (e.g., body mass and other phenotypic traits). It follows a discussion about many statistical issues underlying the structure of M, including spatial and phylogenetic patterns in data and translations between assemblage and cross-species patterns. Matrix M can also be divided into several submatrices using species-level data in a deconstruction approach. Finally, it is interesting to discuss problems in the primary data sources for filling M and how the biodiversity shortfalls may affect our understanding of macroecological patterns.
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Macroecology is now a successful approach to investigate ecological patterns, providing a way to look at the natural systems “from a distance.” This scientific perspective focuses on the overall and emergent patterns instead of idiosyncrasies and local variation, seeking to understand the ecological and evolutionary processes at lower hierarchical levels underlying such broad-scale patterns. This “macroecological perspective” evolved in at least two partially overlapping research traditions, each following different scientific reasoning on building and evaluating theories and models using various methods. This chapter provides an overview of this scientific perspective and its research traditions, followed by a brief overview of the most frequently analyzed macroecological patterns. We start with a synthetic and operational view of how data can be organized and analyzed, combining species-level variation in body mass, geographic range size, and abundance. Moreover, a common goal is to explain and understand the origin and maintenance of these patterns, thus linking patterns and processes. Nevertheless, to achieve this goal, it is necessary to discuss first what we mean by “explain” and “understand” and what we mean by “processes” and “mechanisms” in the distinct research traditions within macroecology.
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This chapter reviews the conceptual and methodological issues related to latitudinal and elevational gradients of species richness at distinct scales. We start with the debates about the generality of such patterns and the null and neutral expectations defined by the “mid-domain effect” proposed in the early 2000s. We present an integrated framework for the ecological and evolutionary drivers of the richness gradients based on equilibrium and non-equilibrium models. First, this framework helps understand the current richness-climate relationships under distinct processes related to geographical variations in abundance (the minimum population hypothesis), climate stability, and ecological specialization affecting diversification (speciation and extinction) rates. We then move to more methodological discussions on estimating such rates based on State Speciation-Extinction (SSE) models and species diversification (tip rates) metrics. We finish the chapter with an overall view of the computational approaches that have been developed to simulate richness patterns under multiple processes.
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There exists little doubt that the Earth's biodiversity is declining. The Nature Conservancy, for example, has documented that one-third of the plant and animal species in the United States are now at risk of extinction. The problem is a monumental one, and forces us to consider in depth how we expect ecosystems, which ultimately are our life-support systems, to respond to reductions in diversity. This issue — commonly referred to as the diversity–stability debate — is the subject of this review, which synthesizes historical ideas with recent advances. Both theory and empirical evidence agree that we should expect declines in diversity to accelerate the simplification of ecological communities.
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A more general biogeographic theory of island species number is produced by replacing area with a more direct measure of available energy in the models of MacArthur and Wilson and Preston. This theory, species-energy theory, applies to islands that differ in their per-unit-area productivity due to differences in physical environment, such as climate. Examination of data on species number of angiosperms and of land and freshwater birds on islands worldwide, demonstrates that species-energy theory can explain 70-80% of the variation in species number, and further suggests the existence of regular geographic trends in resource utilization or species-abundance patterns. The concepts embodied in species- energy theory can in principle be used to develop predictions of species' abundances and probabilities of occurrence on an island. -from Author
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The latitudinal gradient in species richness, wherein species richness peaks near the equator and declines toward the poles, is a widely recognized phenomenon that holds true for many taxa in all habitat types. Understanding the causative mechanism of mechanisms that generate the latitudinal gradient in species richness (LGSR) has been a major challenge, and the gradient remains unexplained. A different latitudinal trend (named Rapoport's rule), in which the mean size of species geographical ranges tends to decline toward the equator, has been hypothesized by G.C. Stevens to play a key role in generating the LGSR when coupled with a version of the rescue effect, in which local populations toward the fringes of geographical ranges are sustained by immigration. The Stevens hypothesis is now commonly cited as a potential explanation for the LGSR and has provoked numerous empirical studies in macroecology and biogeography. However, important aspects of the hypothesis are not obvious in Steven's verbal model and may go unrecognized, despite their major implications for empirical work related to large-scale ecological and evolutionary processes. Here the authors present mathematical simulation models that test the logical structure of the Stevens hypothesis, examine effects on global patterns of species richness produced by the mechanisms (Rapoport's rule and the rescue effect) explicitly identified by Stevens, and investigate the additional effect of competition.
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Abstract Studies of elevation clines in diversity and composition of ecological communities date back to the origins of biogeography. A modern resurgence of interests in these elevational clines is likely to contribute important insights for developing a more general theory of species diversity. In order to gain a more comprehensive understanding of geographical clines in diversity, the research programme for montane biogeography should include statistically rigorous tests of apparent patterns, comparisons of patterns among regions and taxonomic or ecological groups of species, and analyses of clines in environmental variables concurrent with biogeographical surveys. The conceptual framework for this research programme should be based on the assumption that elevational gradients in species diversity result from a combination of ecological and evolutionary processes, rather than the presumed independent effects of one overriding force. Given that montane ecosystems are hot spots of biological diversity, an expanded and integrated programme for biogeographic surveys in montane regions should provide valuable insights for conservation biologists.
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The equilibrium model of island biogeography developed in the 1960s by MacArthur and Wilson has provided an excellent framework in which to investigate the dynamics of species richness in island and island‐like systems. It is comparable in many respects to the Hardy–Weinberg equilibrium model used in genetics as the basis for defining a point of reference, thus allowing one to discover the factors that prevent equilibrium from being achieved. Hundreds of studies have used the model effectively, especially those dealing with brief spans of time and limited geographical areas. In spite of this utility, however, there are important limitations to the MacArthur–Wilson model, especially when we consider long‐term and large‐scale circumstances. Although their general theory is more complex, the MacArthur–Wilson equilibrium model treats colonization and extinction as the only two processes that are relevant to determining species richness. However, it is likely that phylogenetic diversification (phylogenesis) often takes place on the same time‐scale as colonization and extinction; for example, colonization, extinction, and phylogenesis among mammals on oceanic and/or old land‐bridge islands in South‐east Asia are all measured in units of time in the range of 10 000–1 million years, most often in units of 100 000 years. Phylogenesis is not a process that can be treated simply as ‘another form of colonization’, as it behaves differently than colonization. It interacts in a complex manner with both colonization and extinction, and can generate patterns of species richness almost independently of the other two processes. In addition, contrary to the implication of the MacArthur–Wilson model, extinction does not drive species richness in highly isolated archipelagoes (those that receive very few colonists) to progressively lower values; rather, phylogenesis is a common outcome in such archipelagoes, and species richness rises over time. In some specific instances, phylogenesis may have produced an average of 14 times as many species as direct colonization, and perhaps 36 species from one such colonization event. Old, stable, large archipelagoes should typically support not just endemic species but endemic clades, and the total number of species and the size of the endemic clades should increase with age of the archipelago. The existence of long‐term equilibrium in actual island archipelagoes is unlikely. The land masses that make up island archipelagoes are intrinsically unstable because the geological processes that cause their formation are dynamic, and substantial changes can occur (under some circumstances) on a time‐scale comparable to the processes of colonization, phylogenesis, and extinction. Large‐scale island‐like archipelagoes on continents also are unstable, in the medium term because of global climatic fluctuations, and in the long term because of the geologically ephemeral existence of, for example, individual mountain ranges. Examples of these phenomena using the mammals of South‐east Asia, especially the Philippines, make it clear that the best conceptual model of the long‐term dynamics of species richness in island archipelagoes would be one in which colonization, extinction, and phylogenesis are recognized to be of equivalent conceptual importance. Furthermore, we should expect species richness to be always in a dynamic state of disequilibrium due to the constantly changing geological/geographical circumstances in which that diversity exists, always a step or two out of phase with the constantly changing equilibrium point for species richness.
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Aim To demonstrate a new and more general model of the species–area relationship that builds on traditional models, but includes the provision that richness may vary independently of island area on relatively small islands (the small island effect). Location We analysed species–area patterns for a broad diversity of insular biotas from aquatic and terrestrial archipelagoes. Methods We used breakpoint or piecewise regression methods by adding an additional term (the breakpoint transformation) to traditional species–area models. The resultant, more general, species–area model has three readily interpretable, biologically relevant parameters: (1) the upper limit of the small island effect (SIE), (2) an estimate of richness for relatively small islands and (3) the slope of the species–area relationship (in semi‐log or log–log space) for relatively large islands. Results The SIE, albeit of varying magnitude depending on the biotas in question, appeared to be a relatively common feature of the data sets we studied. The upper limit of the SIE tended to be highest for species groups with relatively high resource requirements and low dispersal abilities, and for biotas of more isolated archipelagoes. Main conclusions The breakpoint species–area model can be used to test for the significance, and to explore patterns of variation in small island effects, and to estimate slopes of the species–area (semi‐log or log–log) relationship after adjusting for SIE. Moreover, the breakpoint species–area model can be expanded to investigate three fundamentally different realms of the species–area relationship: (1) small islands where species richness varies independent of area, but with idiosyncratic differences among islands and with catastrophic events such as hurricanes, (2) islands beyond the upper limit of SIE where richness varies in a more deterministic and predictable manner with island area and associated, ecological factors and (3) islands large enough to provide the internal geographical isolation (large rivers, mountains and other barriers within islands) necessary for in situ speciation.
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Scaling relationships have been a persistent theme in biology at least since the time of Leonardo da Vinci and Galileo. Because scaling relationships are among the most general empirical patterns in biology, they have stimulated research to develop mechanistic hypotheses and mathematical models. While there have been many excellent empirical and theoretical investigations, there has been little attempt to synthesize this diverse but interrelated area of biology. In an effort to fill this void, Scaling in Biology, the first general treatment of scaling in biology in over 15 years, covers a broad spectrum of the most relevant topics in a series of chapters written by experts in the field. Some of those topics discussed include allometry and fractal structure, branching of vascular systems of mammals and plants, biomechanical and life history of plants, invertebrates and vertebrates, and species-area patterns of biological diversity. Many more examples are included within this text to complete the broader picture. Scaling in Biology conveys the diversity, promise, and excitement of current research in this area, in a format accessible to a wide audience of not only specialists in the various sub-disciplines, but also students and anyone with a serious interest in biology.
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The mechanisms of macroevolutionary change have long been a contentious issue. Palaeoecological evidence, presented in this book, shows that evolutionary processes visible in ecological time do not build up into macroevolutionary trends, contrary to Darwin's original thesis. The author discusses how climatic oscillations on ice-age time-scales are paced by variations in the Earth's orbit, and have thus been a permanent feature of Earth history. There is, however, little evidence for macroevolutionary change in response to these climatic changes, suggesting that over geological time macroevolution does not occur as a result of accumulated short term processes. These conclusions are used to construct a post-modern evolutionary synthesis in which evolution and ecology play an equal role. Written by a leading palaeoecologist, this book will be of interest to researchers in both ecology and evolutionary biology.
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A 1961-90 mean monthly climatology for Africa south of the Equator was constructed at a resolution of 0.5° latitude/longitude for a suite of eight surface climate variables: minimum, maximum and mean air temperature; rainfall; sunshine hours; vapour pressure; wind speed; and rain day (>0.1 mm)frequencies. This climatology was constructed from observed station data distributed across the region with station frequencies ranging from 288 (wind speed) to 916 (rainfall). Over 92% of these data is based on observations between 1961-90 and over 85% has been supplied by national meteorological agencies from the region. Additionally, for mean temperature and rainfall, monthly anomalies with respect to the 1961-90 average have been calculated at the same spatial resolution for each month from January 1961 to December 1994. This paper describes the dataset which has been compiled for this work, the interpolation methods which have been used, together with some assessment of the accuracy of the resulting climate surfaces. The interpolation of the 1961-90 normals uses elevation, as well as longitude and latitude, as predictor variables and this enables three climate surfaces to be constructed for each variable, reflecting the 'minimum', mean and 'maximum' elevation within each 0.5° cell. The interpolation of the anomaly fields uses a simpler method in which elevation is not considered. These anomaly time series enable fields of interannual variability to be established for mean temperature and rainfall. The second part of the paper uses this climatology to construct fields of mean monthly potential evapotranspiration (PET) for the region using a number of different calculation methods. A comparison of the resulting PET estimates highlights significant spatial and seasonal biases due to differences in climate input variables and in the theoretical representation of PET. The climatology, described and analysed here is available from the authors for use in climate modelling and the study of climate change in Africa south of the Equator.
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This book had its origin when, about five years ago, an ecologist (MacArthur) and a taxonomist and zoogeographer (Wilson) began a dialogue about common interests in biogeography. The ideas and the language of the two specialties seemed initially so different as to cast doubt on the usefulness of the endeavor. But we had faith in the ultimate unity of population biology, and this book is the result. Now we both call ourselves biogeographers and are unable to see any real distinction between biogeography and ecology.
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Island biogeography is the study of the distribution and dynamics of species in island environments. Due to their isolation from more widespread continental species, islands are ideal places for unique species to evolve, but they are also places of concentrated extinction. Not surprisingly, they are widely studied by ecologists, conservationists and evolutionary biologists alike. There is no other recent textbook devoted solely to island biogeography, and a synthesis of the many recent advances is now overdue. This second edition builds on the success and reputation of the first, documenting the recent advances in this exciting field and explaining how islands have been used as natural laboratories in developing and testing ecological and evolutionary theories. In addition, the book describes the main processes of island formation, development and eventual demise, and explains the relevance of island environmental history to island biogeography. The authors demonstrate the huge significance of islands as hotspots of biodiversity, and as places from which disproportionate numbers of species have been extinguished by human action in historical time. Many island species are today threatened with extinction, and this work examines both the chief threats to their persistence and some of the mitigation measures that can be put in play with conservation strategies tailored to islands.
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The distribution of southern Africa's woody flora (N = 1372 species) describes a west-to-east pattern of increasing species richness, being lowest in arid to semi-arid areas and highest in mesic to humid areas. Climate accounts for 77.8% of the variation; species richness is greatest where the amount and duration of energy is optimized and moisture maximized, and decreases as the amount or duration of energy moves above or below optimal conditions, or as moisture decreases. Given the perpetual and necessary relationship between climate and plant photosynthesis, climate provides a first-order, albeit partial, explanation for the persistence of pattern (especially latitudinal and elevation gradients) in the distribution of woody plant species richness over space and time. -Author
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The patterns of species richness in the south-western Cape Province, South Africa, at a quarter-degree scale are documented for several plant taxa typical of the Cape flora, i.e. Restionaceae, Ericaceae, Proteaceae, Pentaschistis (Nees) Stapf (Poaceae) and Aspalathus L. (Fabaceae). The patterns of species richness are very similar for all taxa investigated. These patterns are correlated to a range of environmental factors: precipitation, altitude, substratum and vegetation type. It is shown that total precipitation is the best predictor for the patterns of species richness, but that this is to some extent correlated with the range of precipitation and the altitude range. To test for the effect of individual factors, selected samples in which One environment factor varied, were compared. This clearly showed that rainfalls is the best predictor. The number of substrate types, curiously, is not strongly correlated to the patterns of species richness.
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A pollen atlas of Europe is used to estimate the taxonomic diversity (taxon richness) of woody plants between 40⚬ N and 70⚬ N between 13,000 and 1000 years before the present (Y.B.P.). A gradient of decreasing taxonomic diversity with increasing latitude has existed for woody plants in Europe since 13,000 Y.B.P. The slope of this diversity gradient increased through the Holocene and was half as steep 13,000 years ago as it was 1000 Y.B.P. The slope of the diversity gradient increased with time after the retreat of the ice sheet because the colonization rate for new woody taxa was higher in southern Europe than in northern Europe. An equilibrium pattern of taxon richness may have been reached 6000 Y.B.P. These results support the hypothesis that modern differences in the diversity of woody plants between higher and lower latitudes in Europe are mostly a consequence of contemporary climatic limits rather than of differences in the time available for colonization since the retreat of the ice sheet.
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Germination trials were carried out on surface and buried soil samples from the Krakatau islands, with the aim of characterizing the nature and variability of the short-term seed bank and the potential significance of long-term subsurface seed storage. Thirty-six species of seed plants representing the Krakatau flora germinated from the samples. The topsoil samples yielded the largest number of seedlings and species, and had a faster pace of germination. These samples were found to be locally similar to each other but disharmonic with the extant vegetation. Seeds germinated both from samples buried by land crabs and from soils buried by layers of volcanic ash deposited ca 1930-33 and 1952-53. Eleven species of seed plants germinated from four samples buried ca 1930-33, indicating that these seeds survived burial by volcanic ash for ca 60 years.
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Species richness of six pasture arthropod assemblages (total arthropod species, total herbivore species, sucking and chewing herbivores, total predatory species and spiders) were regressed against several geographical variables (area, distance from the nearest mainland, maximum elevation and geological age of the islands) of three Azorean islands (S. Maria, Terceira and Pico). The species were sampled by the fixed-quadrat size sampling method and the results obtained are consistent with the geological age hypothesis, i.e. the species richness of the six indigenous arthropod assemblages increases with the geological age of the islands, both at local and regional scales. Higher values of indigenous and endemic species richness were consistently found on the older island (S. Maria), and the lowest values on the most recent island (Pico). Moreover, when considering the age of Faial (an older island probably once connected with Pico) as a estimate of the age of Pico, correlations between species richness and island age were improved, thereby strengthening the relationship. The older island (S. Maria) has more specialized herbivores and a greater proportion of herbivores in relation to predatory arthropods. Ecological and biogeographical studies in the Azores should take into account the effects of the time each island has been available for colonization and evolution.
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Hierarchy theory assumes that many ecological properties can be best interpreted by an investigation in other scales than by keeping only at the scale where they are observed. Six examples going from larger to smaller scales illustrate this approach. 1) The debate about the relations between speciation by vicariance or speciation by dispersion. 2) A demonstration of the necessity to refer to the historical development of bird faunas in order to explain modern biogeographical patterns of distribution of birds in Mediterranean forests. 3) Challenges the hypothesis of ecomorphological convergence of bird communities composed of unrelated taxa living in similar mediterranean bioclimates. 4) Processes of community organization and regulation of regional diversities of forest birds in relation to the structure and the geographical configuration of habitats. Extinction-immigration processes are very different whether the habitat is surrounded by a deep primeval forest or is an isolated woodlot. 5) The role of history and man on colonization patterns and the structure of island communities. Probability of successful colonization largely depends on species-specific histories, whether the species evolved in large tracts of homogeneous habitats or in small isolated habitats. Insular patterns of mammal communities in the Mediterranean islands cannot be explained by current theories of island biogeography because all the present species have been introduced by man in the last 8000yr. 6) The consequences of modifications of the structure of insular bird communities are explored at the level of life histories of selected species. The tradeoff of such important life history traits as the timing of reproduction, the clutch size and survival values is better explained by a detailed study of local environmental conditions than by current theories of island biogeography and demographic strategies.-from Author
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What is biodiversity? Part 1 Measuring biodiversity: genetics of biological diversity - from varieties to species comparing character diversity among biotas species richness - measure and measurement measuring relations among biodiversity, ecological function and functional diversity diversity and higher-levels of organization. Part 2 Patterns in biodiversity: spatial and temporal patterns of genetic diversity within species spatial patterns in taxonomic diversity temporal changes in biodiversity - detecting patterns and identifying causes spatial and temporal patterns in functional diversity. Part 3 Conservation and management: does biodiversity matter? - evaluating the case for conserving species identifying priorities for the conservation of biodiversity - systematic biological criteria within a socio-political framework managing biodiversity biodiversity and global change.
Chapter
This book is a unique collection of evolutionary and ecological perspectives in the study of biodiversity by some of the leading researchers in the field. The seventeen chapters are divided into three sections, each section beginning with an overview of its contents. The book traces past landmarks, current questions, and future trends in biodiversity reseach ranging from the evaluation of the fossil record and molecular phylogenies in untangling the genesis of diversity; to population, community, and ecosystem-level approaches in understanding patterns of species persistence; and finally to large-scale diversity patterns and species conservation. Subject reviews, case-studies, and discussions of techniques are combined to produce a state-of-the-art book.
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1 The number of woody species in tropical forests tends to increase with precipitation, forest stature, soil fertility, rate of canopy turnover and time since catastrophic disturbance, and decrease with seasonality, latitude, altitude, and diameter at breast height (d.b.h.).2 A model is presented to account for these trends. Novel hypotheses include how increased rainfall and substrate fertility, and decreased seasonality, might (i) increase attacks by natural enemies, and thus the overall level of density-dependent plant mortality; (ii) increase shade tolerance, canopy turnover, and stem density of the species-rich understorey; and (iii) increase reliance on relatively sedentary forest-interior birds for seed dispersal, fostering high rates of speciation in understorey genera.3 High rainfall and low seasonality in the tropics favour two key groups of natural plant enemies – insects and fungi – that are directly responsible for promoting high rates of density-dependent plant mortality. Lower rainfall, greater seasonality, soil infertility, or unfavourable rooting conditions favour greater allocation to anti-herbivore defences, and thus lead to lower rates of such mortality and thence to lower tree diversity. The increased number of individuals on rainier sites is a minor contributor to increased tree diversity, accounting for only about 17% of the 8.3-fold increase with rainfall in the lowland Neotropics.4 Predictions of the model are consistent with many ecological patterns of variation in tropical tree diversity within regions, and may help explain the decrease in tree diversity with elevation and the accompanying decrease in horizontal patchiness (within-habitat  diversity).5 Random drift over evolutionary time in the relative effectiveness of density-dependent control of individual tree species by specialized natural enemies may better account for the observed distribution of tropical tree abundance than a random walk of species abundance through ecological time.
Article
We analysed a 50-year dataset of avian species observations to determine how richness and community composition varied over a period of landscape-scale environmental change. Our study area, northern lower Michigan, has experienced substantial land-use and land-cover change over time. Like much of the northern Midwest, it has shifted from a largely unpopulated, post-logging shrubland to a moderately populated closed-canopy forest. Such changes are generally expected to influence overall richness and community composition. We found that regional richness per year remained virtually unchanged over the study period. Year-to-year variation in species number was surprisingly low. Richness totals included vastly different species groups as the composition of the regional bird community changed substantially over time. Changes in the types of species present appear to reflect deterministic changes in habitat. The number of grassland and open-habitat species decreased, for example, while species associated with older forests and urban habitats increased. Our results suggest that habitat changes at the landscape scale do not necessarily lead to changes in the number of species a region can support. Such changes, however, do appear to influence the types of species that will occupy a region, and can lead to substantial changes in community composition.
Article
Species richness of six pasture arthropod assemblages (total arthropod species, total herbivore species, sucking and chewing herbivores, total predatory species and spiders) were regressed against several geographical variables (area, distance from the nearest mainland, maximum elevation and geological age of the islands) of three Azorean islands (S. Maria, Terceira and Pico). The species were sampled by the fixed‐quadrat size sampling method and the results obtained are consistent with the geological age hypothesis, i.e. the species richness of the six indigenous arthropod assemblages increases with the geological age of the islands, both at local and regional scales. Higher values of indigenous and endemic species richness were consistendy found on the older island (S. Maria), and the lowest values on the most recent island (Pico). Moreover, when considering the age of Faial (an older island probably once connected with Pico) as a estimate of the age of Pico, correlations between species richness and island age were improved, thereby strengthening the relationship. The older island (S. Maria) has more specialized herbivores and a greater proportion of herbivores in relation to predatory arthropods. Ecological and biogeographical studies in the Azores should take into account the effects of the time each island has been available for colonization and evolution.
Article
Palaeoecological insights have had only a limited impact on modern ecological thinking, and tend to be used in an unsophisticated manner. Recent successes in correlating tree diversity with contemporary climate and, in particular, energy, have led to claims that explanations for tree diversity based on historical processes or events are superfluous. However, diversity-energy correlations are strong only at regional scales, and fail to predict diversity at small plots within latitudinal bands, or between continents. Moreover, tree diversity cannot have responded to global glacial-interglacial energy fluctuations because plant species cannot evolve that rapidly nor, in most areas of the world, can migration plausibly adjust regional floral diversity. Thus contemporary climate or energy, while yielding excellent correlations with plant diversity, has no explanatory power. Palaeoecological studies show that cycles of forest migration, fragmentation, reduction, and re-expansion are forced by glacial-interglacial climate cycles at high to mid latitudes. These in turn reduce opportunities for habitat specialization, rapidly eliminate species that remain rare throughout a glacial-interglacial cycle, and promote genetic continuity between populations. The result is increasingly impoverished regional floras with increasing latitude, and hence the latitudinal tree species gradient. Contemporary climate regimes act as a surrogate for the sum total of past climatic states and their effects on diversity, and hence the strong regional climate correlations with tree diversity.
Article
For the first time, Holocene macroremains (cones and wood) of Larix sibirica Ledeb., radiocarbon dated between 8700 and 7500 BP, have been recovered from two sites in the Scandes Mountains of Sweden. The sites are separated by >300 km and lie in the present subalpine and low alpine belts, respectively. Existing pollen-stratigraphical records have not suggested the presence of Larix in the Holocene beyond its present range, i.e. >1000 km to the east in Russia. Hence, the pollen analytical method should be used more cautiously when inferring subcontinental-continental biogeographical dynamics. It appears that Larix immigrated rapidly by longdistance jump dispersal soon after the deglaciation. The same pattern has emerged for Picea abies (L.) Karst. and some thermophilous broadleaved tree species. This might be a more general mechanism for tree spread during the early Holocene. Step-wise migration and migrational lags could be quite unimportant elements within tree palaeobiogeography. This increases the prospects for interpretation of longterm and large-scale changes in plant cover performance in terms of expansion/decline relative to climatic change. Today, Larix sibirica prospers in continental climates with extremely cold winters, thus it is reasonable to infer that early-Holocene winters in western Fennoscandia could have been similar to, or slightly colder than those of today. This contention conflicts with previously published simulations using General Circulation Models, pollen-climate response surfaces and other retrospective devices, which suggest a strongly oceanic climate with winters >2<sup>⚬</sup>C warmer than present.
Article
Tactics for conserving biodiversity in fragmented communities have been preoccupied with how to preserve intact and unchanged remnants of the original communities. I suggest that this objective is probably unrealistic for the small fragments that will comprise most elements of future systems, and propose that conservation needs to concern itself more with species preservation in the entirely new situations that these small-fragment systems provide. The inherent flexibility of most plants, the possibility that many plant communities are un-saturated, and limited data from a few long-isolated community fragments, provide some cause for cautious optimism in this endeavour. The latter data suggest that large numbers of plant species can coexist in small fragments, albeit in combinations and structures that may seem `unnatural' in the context of continuous communities; I suggest that a refocusing of research on these as new systems, rather than as microcosms of pre-existing continuous systems, is needed.
Article
There are few established laws in ecology. Most ecologists have to contend with systems of bewildering complexity, in which it is hard to separate the wood from the trees. Scientific disciplines without a good framework of rules and laws are generally considered the poor relations of their ilk, and, as human impacts on our planet appear to have reached alarming levels, the need for reliable ecological theory is hard to overstate. The discovery and demonstration of new laws in ecology — such as the Universal Growth Law for plants described by Enquist et al.1 on page 907 of this issue — is thus particularly noteworthy.
Article
Predictable geographic patterns in the distribution of species richness, especially the latitudinal gradient, are intriguing because they suggest that if we knew what the controlling factors were we could predict species richness where empirical data is lacking (e.g. tropics). Based on analyses of the macro-scale distribution of woody plant species richness in Southern Africa, one controlling factor appears to be climate-based water-energy dynamics. Using the regression models of climate's relationship to species richness in Southern Africa, I was able to describe an Interim General Model (IGM) and to predict first-order macro-scale geographic variations in woody plant species richness for the continent of Africa, as well as elsewhere in the world—exemplified using South America, the United States and China. In all cases, the geographic pattern of variation in species richness is in accord with geographic variations in vegetation (visual comparison with vegetation maps) and net primary productivity. What validation was possible (Africa and U.S.A.) suggests that the IGM provides ‘reasonable’ estimates for actual woody plant species richness where species richness is in relative equilibrium with climate. Areas of over- or under-prediction support the contention of earlier workers that edaphic, topographic, historical, and dispersal factors need to be considered in a more complete explanation for spatio-temporal variations in species richness. In addition to providing a means for systematically estimating woody plant species richness where present-day empirical data is lacking, the Interim General Model may prove useful for modelling the effects of climate change (past/future) on species richness (and, by association, the vegetation).
Article
The spatial patterns of canopy tree and seedling life stages in the African Tropical Tree Miliciaexcelsa were examined to test the JanzenConnell hypothesis states that the mortality of seeds and seedlings is highest near the adult tree and declines with distance away from the adult tree of the same species. This hypothesis argues that this effect is partially responsible for maintaining the high tree species diversity of tropical forests. Solar radiation and fruit dispersal were investigated as possible explanations of observed patterns in seedling distribution. Miliciaexcelsa trees [greater-than-or-equal]30 cm DBH were found to be randomly dispersed and occurred at a density of [less-than-or-equal]1 ha. Miliciaexcelsa seedlings were located in small clumps between parent trees and up to 150 m from parents at a mean density of 65 seedlings ha29% of full irradiance. Planted seedlings did not suffer greater mortality closer to adult conspecifics, and survived at light levels between 2–37% of full irradiance. Phytolyma spp., gall-forming psyllids which cause high mortality in Milicia seedlings in large openings and plantations, were not observed on any natural or planted seedlings, although galls were present in the crowns of dominant trees.
Article
The latitudinal gradient in species richness is paralleled by a latitudinal gradient in geographical-range size called Rapoport's rule. The greater annual range of climatic conditions to which individuals in high-latitude environments are exposed relative to what low-latitude organisms face may have favored the evolution of broad climatic tolerances in high-latitude species. This broad tolerance of individuals from high latitudes has led to wider latitudinal extent in the geographical range of high-latitude species than of lower-latitude species. If low-latitude species typically have narrower environmental tolerances than high-latitude species, then equal dispersal abilities in the 2 groups would place more tropical organisms out of their preferred habitat than higher-latitude species out of their preferred habitat. A larger number of "accidentals' (species that are poorly suited for the habitat) would thus occur in tropical assemblages. The constant input of these accidentals artificially inflates species numbers and inhibits competitive exclusion. -from Author