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	<title>spatial ecology &#8211; Science</title>
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	<title>spatial ecology &#8211; Science</title>
	<link>https://scienmag.com</link>
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		<title>Continuous and asymmetric dorsal–ventral abundance associations along the wing in feather mite communities</title>
		<link>https://scienmag.com/continuous-and-asymmetric-dorsal-ventral-abundance-associations-along-the-wing-in-feather-mite-communities/</link>
		
		<dc:creator><![CDATA[Drew Townsend]]></dc:creator>
		<pubDate>Tue, 20 Oct 2026 12:15:20 +0000</pubDate>
				<category><![CDATA[Biology]]></category>
		<category><![CDATA[asymmetric]]></category>
		<category><![CDATA[asymmetry in feather mite communities]]></category>
		<category><![CDATA[bird parasites]]></category>
		<category><![CDATA[community assembly]]></category>
		<category><![CDATA[continuous]]></category>
		<category><![CDATA[continuous within-host parasite variation]]></category>
		<category><![CDATA[Dorsal]]></category>
		<category><![CDATA[dorsal and ventral surface mite relationships]]></category>
		<category><![CDATA[dorsal-ventral abundance associations]]></category>
		<category><![CDATA[ectosymbionts]]></category>
		<category><![CDATA[feather mite distribution patterns]]></category>
		<category><![CDATA[feather mite spatial distribution]]></category>
		<category><![CDATA[feather mites]]></category>
		<category><![CDATA[feather remiges and mite ecology]]></category>
		<category><![CDATA[host individual variation in mite distribution]]></category>
		<category><![CDATA[host-parasite relationships]]></category>
		<category><![CDATA[mixed-effects models]]></category>
		<category><![CDATA[nonlinear mixed-effects models in parasitology]]></category>
		<category><![CDATA[positional variation in mite abundance]]></category>
		<category><![CDATA[Siberian Rubythroat]]></category>
		<category><![CDATA[Siberian Rubythroat feather mites]]></category>
		<category><![CDATA[spatial ecology]]></category>
		<category><![CDATA[wing morphology]]></category>
		<category><![CDATA[wing position gradient in mites]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=318589</guid>

					<description><![CDATA[A study of Siberian Rubythroat found that dorsal and ventral feather mite abundances were associated differently across wing positions, with the pattern detected in adults but not juveniles.]]></description>
										<content:encoded><![CDATA[<p>Feather mite communities on the wings of Siberian Rubythroats showed different patterns of dorsal and ventral abundance depending on position along the wing. An analysis of individual feathers found that the dorsal mite Trouessartia calliope was largely absent from the distal outer remiges, or flight feathers, and increased toward remiges closer to the body. The ventral mite Proctophyllodes sp. also exhibited a positional gradient.</p>
<p>When all positions were averaged, dorsal and ventral abundances were only weakly associated, but position-specific models revealed a stronger and changing relationship. The researchers examined feather-level spatial abundance associations along the proximodistal axis of the wing in Siberian Rubythroat, Calliope calliope . This axis extends from the innermost feathers near the body toward the outermost flight feathers.</p>
<p>Using nonlinear mixed-effects models, they assessed how the abundance of the two mite taxa varied among positions and whether mites on the dorsal and ventral surfaces followed associated patterns. The study addressed continuous variation within a host rather than dividing the wing into separate regions, allowing the relationship between the two surfaces to be assessed at multiple locations. The fitted dorsal–ventral slope was positive in the distal outer remiges, declined toward positions in the middle of the wing, and approached a weakly negative value in the innermost secondaries.</p>
<p>The authors caution that positive slopes in the distal outer remiges should not be taken as evidence of stable coexistence between the mite taxa. Because dorsal abundance was minimal in that region, the pattern may reflect responses to environmental constraints associated with distal wing positions rather than a persistent association between the two mites. This position-dependent pattern was detected in breeding adult birds but not in juveniles.</p>
<p>The researchers suggest that the difference may reflect age-related variation in within-host spatial organization. Juvenile birds may have had less time since mite transmission for their communities to assemble, whereas the pattern in adults may be more established. The analysis does not establish age as the direct cause or identify the mechanisms responsible.</p>
<p>In both age groups, mite abundances were bilaterally symmetrical, indicating broadly similar abundance on corresponding feathers of the left and right wings. The study also found no consistent effects of sex, date, or year. Together, the findings show that feather mite assemblages can be spatially heterogeneous even within a single host.</p>
<p>Pooling positions across the wing produced only weak overall dorsal–ventral associations, while the position-specific analysis revealed a relationship that ranged from positive to weakly negative. The results do not demonstrate that either mite taxon benefits from the presence of the other, nor do they show that one taxon causes changes in the abundance of the other. Instead, the study identifies wing position and bird age as important factors to consider when analyzing within-host mite communities, while bilateral symmetry and the absence of consistent date, year, or sex effects suggest a relatively stable spatial template associated with the host’s wing morphology.</p>
<p><strong>Subject of Research:</strong> Spatial variation in dorsal and ventral feather mite abundance across Siberian Rubythroat wings</p>
<p><strong>Article Title:</strong> Continuous and asymmetric dorsal–ventral abundance associations along the wing in feather mite communities</p>
<p><strong>Article References:</strong> Takagi, M., Iwasaki, M., Yasuda, N., Shiraiwa, S., Katoh, T., &amp; Takaku, G. (2026). Continuous and asymmetric dorsal–ventral abundance associations along the wing in feather mite communities. <em>The Science of Nature, 113</em>(6), Article 137. <a href="https://doi.org/10.1007/s00114-026-02182-4" rel="noopener noreferrer">https://doi.org/10.1007/s00114-026-02182-4</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.1007/s00114-026-02182-4" rel="noopener noreferrer">10.1007/s00114-026-02182-4</a></p>
<p><strong>Keywords:</strong> feather mites, Siberian Rubythroat, spatial ecology, host-parasite relationships, wing morphology, mixed-effects models, community assembly, ectosymbionts, bird parasites, Continuous, asymmetric, dorsal</p>
]]></content:encoded>
					
		
		
		<post-id xmlns="com-wordpress:feed-additions:1">318589</post-id>	</item>
		<item>
		<title>Camera traps estimate male ocelot ranges in one Brazilian forest reserve</title>
		<link>https://scienmag.com/camera-traps-estimate-male-ocelot-ranges-in-one-brazilian-forest-reserve/</link>
		
		<dc:creator><![CDATA[Margaret Porter]]></dc:creator>
		<pubDate>Tue, 20 Oct 2026 11:53:44 +0000</pubDate>
				<category><![CDATA[Biology]]></category>
		<category><![CDATA[Science News]]></category>
		<category><![CDATA[Atlantic Forest]]></category>
		<category><![CDATA[Brazil Atlantic Forest conservation]]></category>
		<category><![CDATA[Brazilian forest reserve biodiversity]]></category>
		<category><![CDATA[camera trap methodology in tropical forests]]></category>
		<category><![CDATA[Camera trap ocelot home range estimates]]></category>
		<category><![CDATA[camera traps]]></category>
		<category><![CDATA[ecological monitoring of elusive species]]></category>
		<category><![CDATA[Espírito Santo]]></category>
		<category><![CDATA[habitat use of solitary felids]]></category>
		<category><![CDATA[home range]]></category>
		<category><![CDATA[Kernel Density Estimation]]></category>
		<category><![CDATA[latrines]]></category>
		<category><![CDATA[Leopardus]]></category>
		<category><![CDATA[Leopardus pardalis]]></category>
		<category><![CDATA[lowland forest ecosystem research]]></category>
		<category><![CDATA[ocelot]]></category>
		<category><![CDATA[ocelot population dynamics]]></category>
		<category><![CDATA[pardalis]]></category>
		<category><![CDATA[protected area biodiversity studies]]></category>
		<category><![CDATA[rainforest animal movement patterns]]></category>
		<category><![CDATA[remote sensing wildlife monitoring]]></category>
		<category><![CDATA[spatial analysis of carnivore territories]]></category>
		<category><![CDATA[spatial ecology]]></category>
		<category><![CDATA[wildlife monitoring]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=318463</guid>

					<description><![CDATA[A year of camera-trap monitoring at eight latrines in Espírito Santo produced mean home-range estimates of 12.08 ± 4.43 and 19.95 ± 9.49 square kilometres for three adult male ocelots using two spatial methods.]]></description>
										<content:encoded><![CDATA[<p>A year-long camera-trap study in a remnant of Brazil’s Lowland Atlantic Forest estimated the home ranges of three adult male ocelots at Vale Natural Reserve in Espírito Santo. Depending on the spatial method used, the three estimates ranged from 6.19 to 38.92 square kilometres. The mean was 12.08 ± 4.43 square kilometres with a 100% minimum convex polygon and 19.95 ± 9.49 square kilometres with a 95% adaptive kernel density estimator. The study identified 22 ocelots in total, but home ranges could be calculated only for males recorded at more than two of the eight monitored latrines, meaning the estimates describe a small subset of the population and only part of the area used by those animals.</p>
<p>The research was conducted at Vale Natural Reserve, a 22,711-hectare protected area between the municipalities of Linhares and Jaguaré in northern Espírito Santo. The reserve forms part of the Linhares-Sooretama Forest Block, which covers more than 53,000 hectares and represents about 11% of the forest remaining in the state. Most of Vale Natural Reserve consists of dense lowland forest on flat terrain, classified as perennial seasonal forest. The landscape also includes a locally named sandy-soil forest type called Mussununga, native grasslands, flooded swamps and areas affected by human uses. The climate is tropical with a dry winter, with a mean annual temperature of 24.3 °C and mean annual rainfall of 1,214 millimetres, although rainfall varied considerably among years.</p>
<p>Researchers collected data at eight ocelot latrines distributed across the reserve. These sites were identified through active searches and characterized by the repeated accumulation of feces and urine in the same location. One Bushnell Trophy Cam HD Agressor digital camera trap was installed on a tree stem facing each latrine. The cameras operated continuously for 24 hours a day from March 2018 to February 2019. At each trigger, they recorded two photographs and a 20-second video, with a 10-second interval between consecutive capture events. The design concentrated observations on sites that ocelots used for scent marking and that the source identifies as places of direct and indirect interaction within and between the sexes.</p>
<p>Ocelots were identified individually from their distinctive coat patterns, including spots and stripes. External sexual characteristics visible in males, together with relative body size, allowed the researchers to classify individuals by sex and age category. The records included eight adult males, 12 adult females and two cubs whose sex was not determined. Both flanks were recorded for six adult males, while only the right flank was available for two; all adult females were recorded on both flanks. Adult males appeared at every latrine, whereas females appeared at all but one. Seven of the eight latrines registered individuals of both sexes, and the two cubs were recorded at one of the eight sites.</p>
<p>Repeated detections at multiple latrines distinguished the spatial records of males from those of females. Six of the eight adult males were recorded at more than one latrine, and three males were each recorded at three sites, qualifying them for home-range estimation. All adult females were recorded at only one site, including the female observed with her two cubs. Males also shared latrines more frequently: the mean number of males recorded per latrine was 2.1, compared with 1.5 females, and five latrines contained more males than females. The observed adult sex ratio was 1.0 male to 1.5 females, unlike an earlier survey at the same reserve that registered more males. The authors suggested that the difference may partly reflect sampling design, because latrines are used for interactions and may have favored the recording of females, but the study did not directly establish the population’s true sex ratio.</p>
<p>Home-range size was estimated in two ways so the results could be compared with published studies that used different analytical approaches. The 100% minimum convex polygon, abbreviated MCP, produced estimates of 6.19 square kilometres for male Lp26, 20.76 square kilometres for Lp44 and 9.28 square kilometres for Lp65. The 95% adaptive kernel density estimator, abbreviated 95%K and calculated with a standard biweight or quartic kernel, produced respective estimates of 10.10, 10.83 and 38.92 square kilometres. The mean 95%K estimate was 1.6 times the mean MCP estimate. The 38.92-square-kilometre kernel estimate for Lp65 was also the largest individual value, showing that the range across the three males and the two methods extended from 6.19 to 38.92 square kilometres rather than being confined to the narrower interval between the smallest and largest polygon estimates.</p>
<p>Vale Natural Reserve’s estimates fell within the range reported for ocelots elsewhere. The source describes published home ranges across the species’ distribution as varying from 2 to 39 square kilometres and cites a meta-analysis with a species-wide mean of 17.4 ± 3.7 square kilometres and a male mean of 20.7 ± 6.1 square kilometres. Previous Atlantic Forest studies using MCP produced mean male estimates of 7.5 ± 4.8 square kilometres in Caraguatá Ecological Reserve in Santa Catarina, 13.4 ± 8.0 square kilometres in the Green Corridor of Misiones in Argentina, and 32.9 ± 10.9 square kilometres in Iguaçu National Park in Paraná. One previous study using 95%K reported a male mean of 45.2 ± 4.9 square kilometres at Iguaçu National Park. The Vale polygon estimate was near the middle of the MCP values reported for the biome, while its kernel estimate was almost half the previously reported kernel mean for male ocelots in Atlantic Forest.</p>
<p>Home-range estimates can vary with sex, age, population density, season, food availability and habitat conditions, but the present study did not measure all of these variables directly. The authors placed the perennial seasonal forest at Vale Natural Reserve between dense ombrophilous forest and dense subtropical semideciduous forest in a vegetation gradient, noting that the reserve’s polygon estimate was intermediate between the lower values reported for ombrophilous forest and the higher value reported for semideciduous forest. They suggested that vegetation structure could affect productivity and prey availability, with smaller ranges potentially associated with greater food availability. That interpretation was based on the reserve’s result together with published values from other sites; the study did not measure prey abundance or establish a general inverse relationship between food availability and ocelot home-range size.</p>
<p>Behavioral interpretations were likewise presented in the context of previous ocelot research. The broader overlap among male records and the lower overlap among female records were consistent with studies in which males occupy larger ranges, although access to females can also influence male movement. The authors cited observations that pregnant and lactating females may increase patrolling and scent marking, potentially making them less tolerant of territorial overlap with other females. Relaxed territoriality among familiar females outside breeding periods, or possible family relationships, were proposed as possible explanations for four adult females using the same latrine, including the female with cubs. These explanations were not tested directly, so they remain interpretations rather than measured causes of the observed distribution.</p>
<p>The study’s central contribution is a paired set of home-range estimates for three adult male ocelots in Lowland Atlantic Forest, accompanied by population and spatial records for 22 identified animals at eight latrines. Its limitations are substantial: only males appearing at more than two latrines received range estimates, the sample comprised three individuals, and the eight monitoring points did not cover the full landscape available to them. The authors therefore described the calculated areas as portions of the total ranges used by the males. Within that scope, the results show that estimates from the same three animals varied markedly with method and place Vale Natural Reserve within the range of previously published ocelot home-range measurements. They also identify latrines as effective monitoring locations for gathering information on ocelot population and spatial ecology, providing reference values for this reserve, the wider Linhares-Sooretama block and comparable lowland forest.</p>
<p><strong>Subject of Research:</strong> Camera-trap estimation of male ocelot home ranges in southeastern Brazil’s Lowland Atlantic Forest</p>
<p><strong>Article Title:</strong> ﻿Ocelot, Leopardus pardalis ( Mammalia , Carnivora , Felidae ), home range in the Lowland Atlantic Forest of Southeastern Brazil</p>
<p><strong>Article References:</strong> Magalhães, L. M., &amp; Srbek-Araujo, A. C. (2022). ﻿Ocelot, Leopardus pardalis (Mammalia, Carnivora, Felidae), home range in the Lowland Atlantic Forest of Southeastern Brazil. <em>Neotropical Biology and Conservation, 17</em>(4), 229-237. <a href="https://doi.org/10.3897/neotropical.17.e93828" rel="noopener noreferrer">https://doi.org/10.3897/neotropical.17.e93828</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.3897/neotropical.17.e93828" rel="noopener noreferrer">10.3897/neotropical.17.e93828</a></p>
<p><strong>Keywords:</strong> ocelot, Leopardus pardalis, home range, camera traps, Atlantic Forest, spatial ecology, wildlife monitoring, Espírito Santo, latrines, kernel density estimation, Leopardus, pardalis</p>
]]></content:encoded>
					
		
		
		<post-id xmlns="com-wordpress:feed-additions:1">318463</post-id>	</item>
		<item>
		<title>Beta diversity peaks at regional scales across ants, birds, diatoms and trees</title>
		<link>https://scienmag.com/beta-diversity-peaks-at-regional-scales-across-ants-birds-diatoms-and-trees/</link>
		
		<dc:creator><![CDATA[Margaret Porter]]></dc:creator>
		<pubDate>Mon, 19 Oct 2026 15:45:35 +0000</pubDate>
				<category><![CDATA[Earth Science]]></category>
		<category><![CDATA[Science News]]></category>
		<category><![CDATA[and trees]]></category>
		<category><![CDATA[beta]]></category>
		<category><![CDATA[beta diversity]]></category>
		<category><![CDATA[Biodiversity Conservation]]></category>
		<category><![CDATA[biogeography of ants]]></category>
		<category><![CDATA[birds]]></category>
		<category><![CDATA[community scale]]></category>
		<category><![CDATA[cross-taxa comparison]]></category>
		<category><![CDATA[diatoms]]></category>
		<category><![CDATA[dispersal ability influence]]></category>
		<category><![CDATA[diversity]]></category>
		<category><![CDATA[ecological community boundaries]]></category>
		<category><![CDATA[grains]]></category>
		<category><![CDATA[occurs]]></category>
		<category><![CDATA[Peak]]></category>
		<category><![CDATA[Regional]]></category>
		<category><![CDATA[regional species assemblages]]></category>
		<category><![CDATA[Scientific Research]]></category>
		<category><![CDATA[Spatial]]></category>
		<category><![CDATA[spatial ecology]]></category>
		<category><![CDATA[spatial grain analysis]]></category>
		<category><![CDATA[species composition dissimilarity]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=313459</guid>

					<description><![CDATA[For nearly a century, ecologists have argued about whether ecological communities are real, discrete entities in nature or merely convenient abstractions. A new study published in Frontiers of Biogeography offers what may be the most direct empirical answer yet: communities]]></description>
										<content:encoded><![CDATA[<p>For nearly a century, ecologists have argued about whether ecological communities are real, discrete entities in nature or merely convenient abstractions. A new study published in Frontiers of Biogeography offers what may be the most direct empirical answer yet: communities appear to be regional in scale, with the sharpest differences between neighboring assemblages emerging not at local patches but at spatial grains of hundreds to tens of thousands of square kilometers. The finding, drawn from four wildly different groups of organisms across the contiguous United States, could reshape both community ecology and the practice of biodiversity conservation.</p>
<p>The research, led by David Jenkins and colleagues, tackles the question through beta diversity, the measure of how dissimilar two communities are in their species composition. The logic is elegant: if the clearest possible separation between adjacent communities occurs at a particular spatial resolution, then that resolution represents the empirical size of a community. Maximal beta diversity, in other words, marks the scale at which nature draws its sharpest boundaries between assemblages of species.</p>
<p>To test this, the team assembled point data for ants, birds, diatoms, and trees, four taxa chosen for their radically different life histories, dispersal abilities, and data origins. Ant records spanned two centuries of literature synthesis, totaling nearly 25,000 samples and 699 species. Bird data came from the eBird community science platform, with over 810,000 cleaned reports from January and July between 2010 and 2015, standardized as counts per person-hour. Diatoms were sampled from the top five centimeters of lake sediment across 1,070 lakes in a single year, yielding 1,957 species. Tree data, covering stems wider than five centimeters at breast height, came from the US Forest Service&#8217;s Forest Inventory Analysis across four years spaced five years apart, totaling nearly 40,000 samples and 403 species.</p>
<p>The analytical framework organized all georeferenced observations into hexagonal polygons, with cell size defining the spatial grain. At each grain, ranging from one square kilometer to one million square kilometers, the researchers calculated mean pairwise beta diversity between each central hexagon and its immediate neighbors. This neighborhood-based approach, borrowed conceptually from remote sensing research on optimized spatial resolution, controls for sample size across grains because hexagonal grids are constrained to fewer than six neighbors.</p>
<p>A critical methodological decision involved how beta diversity was calculated. The team used a relatively new deviation from a null model based on spatial heterogeneity, called beta NBD for its underlying negative binomial distribution. This measure, developed by Youhua Chen and Fangliang He, represents clustered species patterns more accurately than the older deviation based on spatial homogeneity. The newer measure made only modest adjustments to observed beta diversity and showed no vulnerability to sample size effects, whereas the older measure substantially altered observed values and increased with greater sampling effort.</p>
<p>The results were strikingly consistent. For all four taxa, beta diversity peaked at intermediate, regional spatial grains. Trees showed peak values at roughly 300 square kilometers, remarkably stable across four evaluated years spanning two decades. Winter birds peaked at approximately 500 square kilometers, while summer birds and ants both peaked near 2,000 square kilometers. Diatoms, the microscopic algae inhabiting lake bottoms, showed the largest peak at about 11,000 square kilometers. Hump-shaped quadratic curves fit the data far better than linear models, with Akaike Information Criterion weights exceeding 0.95 in all cases.</p>
<p>These rankings defied the team&#8217;s initial expectations. They had predicted that diatoms, confined to discrete lake habitats, would show the smallest community scales, followed by ants, trees, and birds. Instead, diatoms exhibited the largest peak, and trees the smallest. The researchers suggest that diatom community size roughly matched the average density of sampled lakes across the contiguous US, meaning the apparent regional scale may actually reflect the average dispersion of discrete diatom habitats rather than long-range dispersal. For terrestrial taxa inhabiting intergrading habitats, the regional peaks may reflect genuinely regional processes.</p>
<p>The repeatability of the patterns adds considerable weight to the findings. Bird beta diversity scaling was consistent across six consecutive years, though sensitive to seasonality, with winter communities concentrating at smaller spatial scales than summer ones. Tree patterns showed very little within- or among-annual variation at their peak grain. Given that birds and trees differ so enormously in life history and mobility, this commonality suggests that community assembly processes provide a strong and general basis for the observed regional scaling.</p>
<p>The results broadly support the regional community concept advanced by Robert Ricklefs, who argued in 2008 that regional scales should be preferred to local ones to capture the full suite of selective conditions driving diversity. The relatively low beta diversity at fine spatial grains in this study supports Ricklefs&#8217; argument that local communities are one end of spatiotemporal continua rather than empirically distinct entities. The authors suggest that metacommunity ecology may be wise to treat local communities as sample points rather than bounded units, steering the field toward a species-centric approach.</p>
<p>Beyond its conceptual implications, the work bears fundamental consequences for conservation biogeography in the Anthropocene. If ecological communities are regional in scale, then local conservation efforts can best ensure success when coordinated regionally, through corridors and networks among conserved sites. The findings may also help researchers reconsider the appropriate spatial grains to use when studying diversity responses to land use and climate change, suggesting that rasterized study units matching peak beta diversity would obtain maximal resolution. The authors note that similar peaked spatial scaling may exist for other biogeographical patterns, potentially revealing maximal signal amidst noise and better representing natural patterns than maps designed for visual appeal.</p>
<p><strong>Subject of Research:</strong> Peak beta diversity occurs at regional spatial grains</p>
<p><strong>Article Title:</strong> ﻿Peak beta diversity occurs at regional spatial grains</p>
<p><strong>Article References:</strong> Ohyama, L., Bogota-Gregory, J. D., &amp; Jenkins, D. G. (2024). Peak beta diversity occurs at regional spatial grains. <em>Frontiers of Biogeography, 17</em>, Article e132675. <a href="https://doi.org/10.21425/fob.17.132675" rel="noopener noreferrer">https://doi.org/10.21425/fob.17.132675</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.21425/fob.17.132675" rel="noopener noreferrer">10.21425/fob.17.132675</a></p>
<p><strong>Keywords:</strong> Peak, beta, diversity, occurs, regional, spatial, grains, scientific research</p>
]]></content:encoded>
					
		
		
		<post-id xmlns="com-wordpress:feed-additions:1">313459</post-id>	</item>
		<item>
		<title>Mapping the Urban Wild: How Spatial Ecology Is Redefining City Conservation</title>
		<link>https://scienmag.com/mapping-the-urban-wild-how-spatial-ecology-is-redefining-city-conservation/</link>
		
		<dc:creator><![CDATA[Margaret Porter]]></dc:creator>
		<pubDate>Sat, 17 Oct 2026 06:31:31 +0000</pubDate>
				<category><![CDATA[Biology]]></category>
		<category><![CDATA[Science News]]></category>
		<category><![CDATA[anthropogenic stressors]]></category>
		<category><![CDATA[application of spatial ecology in city conservation]]></category>
		<category><![CDATA[city wildlife habitat mapping]]></category>
		<category><![CDATA[climate change]]></category>
		<category><![CDATA[conservation biology]]></category>
		<category><![CDATA[food attractants in city environments]]></category>
		<category><![CDATA[green infrastructure]]></category>
		<category><![CDATA[green infrastructure for wildlife]]></category>
		<category><![CDATA[habitat fragmentation]]></category>
		<category><![CDATA[human disturbance effects on city wildlife]]></category>
		<category><![CDATA[human-wildlife coexistence]]></category>
		<category><![CDATA[impact of artificial light on urban animals]]></category>
		<category><![CDATA[mixed-species groups]]></category>
		<category><![CDATA[nesting and foraging opportunities in urban areas]]></category>
		<category><![CDATA[One Health]]></category>
		<category><![CDATA[spatial ecology]]></category>
		<category><![CDATA[spatial ecology in cities]]></category>
		<category><![CDATA[urban ecology]]></category>
		<category><![CDATA[urban green corridors]]></category>
		<category><![CDATA[urban habitat fragmentation]]></category>
		<category><![CDATA[urban planning]]></category>
		<category><![CDATA[urban wildlife conservation]]></category>
		<category><![CDATA[water availability for urban species]]></category>
		<category><![CDATA[wildlife corridors]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=294730</guid>

					<description><![CDATA[A new research collection argues that the spatial arrangement of resources, disturbances, and human activity in cities is the key to conserving wildlife in an urbanizing world.]]></description>
										<content:encoded><![CDATA[<p>Cities are often portrayed as ecological dead zones, places where pavement has replaced prairie and where wildlife survives only at the margins. A growing body of research is dismantling that assumption. The second volume of a research collection on the spatial aspects of urban animal ecology and conservation biology, published in Frontiers in Ecology and Evolution, brings together studies spanning amphibians, birds, bats, bears, and mixed-species animal groups, and it delivers a message that is increasingly hard to ignore: the fate of wildlife in the twenty-first century will be decided largely in human-dominated landscapes, and the deciding factor is spatial arrangement.</p>
<p>The collection, edited by Rusty Gonser of Indiana State University together with Ryan Jensen and Steven Petersen of Brigham Young University, builds on a first volume that framed urban animal ecology around broad questions of habitat fragmentation, green corridors, and comparisons between urban and less urbanized environments. Volume II shifts the emphasis from description toward application. Its studies examine how animals respond to specific features of the built environment, including artificial light, green infrastructure, water availability, food attractants, and nesting or foraging opportunities. The unifying theme is that urban conservation depends on understanding where human disturbance, habitat resources, and animal responses intersect on the ground.</p>
<p>One of the most striking reframings in the volume is the treatment of humans as habitat modifiers and urban landscapes as fragmented habitats in their own right. Rather than asking simply whether a species is present in a city or absent from it, the researchers ask how the patchwork of roads, buildings, green spaces, water bodies, and residential neighborhoods shapes movement, habitat use, and avoidance. This mosaic is not static. Climate change adds dynamic disturbances such as urban heat islands and altered water distribution, which continuously redraw the map of usable habitat. Meanwhile, anthropogenic light, sound, and attractants accumulate, further sculpting the sensory landscape through which animals navigate.</p>
<p>Several of the studies move beyond the familiar urban-versus-rural comparison to examine direct and indirect anthropogenic pressures as stressors with physiological consequences. The editors argue that each of these factors should be treated as a potential stressor capable of affecting an organism&#8217;s physiology, morphology, and behavior across its entire lifetime, with downstream effects on reproductive success and therefore on population persistence. Stress, in this view, is not an abstract concept but a measurable biological currency that links the design of a neighborhood to the demographic trajectory of the animals living in it.</p>
<p>A case in point comes from research on the white stork, a species often classified as an urban adapter, meaning it is presumed to tolerate or even thrive alongside human development. The study found elevated stress responses in storks exposed to anthropogenic influences and environmental stressors, demonstrating that even the most adaptable city dwellers are not immune to the pressures of urban life. The finding carries a warning for conservation planning: species labels such as adapter or avoider are not permanent verdicts, and tolerance can erode when the cumulative burden of disturbance crosses physiological thresholds.</p>
<p>The spatial distribution of resources emerges as the volume&#8217;s central practical concern. Whether the resource in question is green infrastructure, open water surfaces, food attractants, nesting sites, or the broader ecosystem services that urban areas provide, the editors argue that effective conservation hinges on knowing where resources are located and how animals actually access them. That kind of landscape data, they contend, should be a prerequisite for conservation policy rather than an afterthought. A corridor that looks connected on a map may be functionally impassable; a pond may be abundant but unreachable; a nesting site may sit in a location that exposes its occupants to lethal levels of disturbance.</p>
<p>Urban planning and design, the editors argue, should incorporate these spatial data to reduce human-animal interactions before they become conflicts. This is complicated by the fact that urban growth can occur rapidly, while species with different natural histories and life histories perceive and respond to habitat modification in markedly different ways. The relative rate of change among urban landscapes matters as well: a city that transforms within a decade presents a fundamentally different selective environment than one that changes incrementally over a century. The editors call for more experimental research on approaches that reduce the attractants drawing wildlife into proximity with people, on ways to identify and modify anthropogenic sources of disturbance, and on the influence of physical clutter on habitat use and avoidance.</p>
<p>The volume also makes a case for rethinking the role of the public in urban ecology. Citizen scientists have traditionally been cast as collectors of presence and absence data, but the editors argue that residents should also be understood as subjects of the data collection. People&#8217;s perceptions of nature influence policy and urban planning, and a community&#8217;s attitude toward a species can matter as much as the species&#8217; biology. Research in the collection suggests that individuals may hold positive perceptions of particular animals, yet communities can still benefit from targeted environmental education that improves knowledge and fosters emotional ties to nature, producing a more conservation-friendly public and, ultimately, better urban management.</p>
<p>Looking forward, the editors advocate a holistic approach that goes beyond indicator species and links the health of all species in an urban landscape across a scale from microbes to animals to humans, in line with a One Health viewpoint. They also highlight a gap in the literature concerning mixed-species groups, the aggregations of different species that forage or move together. There are fitness benefits to membership in such groups, but all participants are exposed to anthropogenic disturbances that could negate those benefits, making mixed-species groups an underexplored unit of urban conservation. The breadth of taxa covered in the volume, from amphibians to bears, suggests that urban conservation biology must move beyond single-species case studies and compare responses across animals with different mobility, habitat needs, and tolerance of disturbance.</p>
<p>The collection closes with a research agenda that reads as a challenge to the field. Which urban design interventions actually improve animal fitness rather than merely animal presence? How do multiple urban stressors interact spatially and synergistically? Can cities be designed as connected habitat networks across taxa? How does urban wildlife respond to habitat changes across seasons and life stages? How can human-wildlife coexistence be measured spatially, and which metrics predict the best outcomes? Which conservation actions can be scaled across cities, and how will climate change reshape urban animal ecology? The overarching question, the editors write, is how spatial urban ecology can identify the specific designs, policies, and community practices that allow animal populations, not just individual animals, to persist in cities under increasing disturbance and a changing climate. The shift they propose, from documenting urban animal responses to testing mechanisms and interventions, may determine whether the next century of urbanization is a story of retreat or one of coexistence.</p>
<p><strong>Subject of Research:</strong> Spatial ecology of animal responses to urban landscapes and its application to urban conservation planning</p>
<p><strong>Article Title:</strong> Editorial: Spatial aspects of urban animal ecology and conservation biology, volume II</p>
<p><strong>Article References:</strong> Gonser, R., Jensen, R., &amp; Petersen, S. (2026). Editorial: Spatial aspects of urban animal ecology and conservation biology, volume II. <em>Frontiers in Ecology and Evolution, 14</em>, Article 2000120. <a href="https://doi.org/10.3389/fevo.2026.2000120" rel="noopener noreferrer">https://doi.org/10.3389/fevo.2026.2000120</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.3389/fevo.2026.2000120" rel="noopener noreferrer">10.3389/fevo.2026.2000120</a></p>
<p><strong>Keywords:</strong> urban ecology, spatial ecology, conservation biology, habitat fragmentation, anthropogenic stressors, green infrastructure, wildlife corridors, urban planning, One Health, mixed-species groups, climate change, human-wildlife coexistence</p>
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		<post-id xmlns="com-wordpress:feed-additions:1">294730</post-id>	</item>
		<item>
		<title>Why Weak Dispersal and Bigger Landscapes Boost Local Biodiversity</title>
		<link>https://scienmag.com/why-weak-dispersal-and-bigger-landscapes-boost-local-biodiversity/</link>
		
		<dc:creator><![CDATA[Margaret Porter]]></dc:creator>
		<pubDate>Fri, 16 Oct 2026 19:52:09 +0000</pubDate>
				<category><![CDATA[Biology]]></category>
		<category><![CDATA[Technology and Engineering]]></category>
		<category><![CDATA[biodiversity]]></category>
		<category><![CDATA[Biodiversity enhancement in fragmented landscapes]]></category>
		<category><![CDATA[competition and coexistence dynamics]]></category>
		<category><![CDATA[competitive exclusion]]></category>
		<category><![CDATA[dispersal]]></category>
		<category><![CDATA[dispersal effects on species coexistence]]></category>
		<category><![CDATA[ecological consequences of weak dispersal]]></category>
		<category><![CDATA[effects of dispersal rates on community homogenization]]></category>
		<category><![CDATA[feasibility domain]]></category>
		<category><![CDATA[habitat fragmentation and species richness]]></category>
		<category><![CDATA[habitat patches]]></category>
		<category><![CDATA[impact of landscape size on ecological communities]]></category>
		<category><![CDATA[landscape ecology]]></category>
		<category><![CDATA[larger landscapes and biodiversity stability]]></category>
		<category><![CDATA[Lotka-Volterra competition]]></category>
		<category><![CDATA[mathematical modeling of ecological communities]]></category>
		<category><![CDATA[metacommunity]]></category>
		<category><![CDATA[metacommunity theory in ecology]]></category>
		<category><![CDATA[microcrustaceans]]></category>
		<category><![CDATA[role of dispersal in local biodiversity]]></category>
		<category><![CDATA[spatial ecology]]></category>
		<category><![CDATA[species coexistence]]></category>
		<category><![CDATA[species coexistence in small habitat patches]]></category>
		<category><![CDATA[theoretical ecology]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=289633</guid>

					<description><![CDATA[A new theoretical study shows that weak dispersal and larger landscapes inevitably increase local biodiversity in competitive metacommunities, a prediction confirmed by long-term data from natural microcrustacean communities.]]></description>
										<content:encoded><![CDATA[<p>One of ecology&#8217;s most persistent puzzles has just received a rigorous theoretical solution. For decades, field ecologists have noticed that species confined to small patches of habitat—connected only loosely by the occasional migrant—somehow manage to coexist locally in greater numbers than theory once predicted. A new study published in PLOS Computational Biology by Frederik De Laender, Andrew Gonzalez, Olivia Bleeckx, Dieter Ebert, and György Barabás now explains why this pattern is not a quirk of particular ecosystems but a mathematical inevitability of competitive metacommunities, and why the effect grows stronger as landscapes get bigger.</p>
<p>To understand why this result matters, it helps to step back and consider how ecologists have traditionally thought about biodiversity in fragmented landscapes. The dominant framework, metacommunity theory, treats a landscape as a collection of local communities linked by the movement of individuals. Within this framework, dispersal has long been recognized as a double-edged force. At low rates, the arrival of new individuals can rescue populations on the brink of local extinction and allow species to persist in patches where environmental conditions would otherwise doom them. At high rates, however, dispersal can homogenize communities, swamp local adaptation, and, in some models, actually undermine coexistence by allowing competitively superior species to flood every patch. The intermediate optimum implied by this tension has been invoked so often that it risks becoming an unexamined assumption. What the new analysis demonstrates is that, for competitive communities in heterogeneous landscapes, the low-dispersal end of this spectrum is not merely one option among many—it is where coexistence is mathematically guaranteed to be promoted, and the strength of that promotion grows predictably with the size of the landscape.</p>
<p>The mathematical heart of the study lies in the spatial extension of Lotka–Volterra competition models, a family of equations that has served as the workhorse of community ecology for nearly a century. In their nonspatial form, these models describe how the growth rate of each species is reduced by its own abundance and by the abundances of competitors, with interaction coefficients capturing the per-capita effect of one species on another. Extending them to a spatial setting means writing a separate equation for each species in each patch, with dispersal terms coupling the equations across patches. Such systems quickly become intractable by exact methods as the number of species and patches grows, which is precisely why the authors turned to analytical approximations. Their approach yields a remarkably compact result: local species persistence can be expressed as a balance between the total density of a species across all patches and its local exclusion rate. In other words, whether a species survives in a given patch depends on how much collective biomass it maintains across the whole landscape versus how strongly the local environment and local competitors push it out.</p>
<p>This reframing has a powerful consequence. It converts a question about a complicated spatial dynamical system into a question about geometry—specifically, about the feasibility domain of the underlying competitive system. The feasibility domain is a concept from nonspatial community ecology: it is the region of parameter space, defined by the species&#8217; intrinsic growth rates and their interaction coefficients, within which all species in a community can maintain positive abundances at equilibrium. A community whose parameters fall deep inside this domain is structurally capable of supporting all its members; one whose parameters fall outside cannot, no matter how the abundances are arranged initially. The authors show that local multispecies coexistence in a heterogeneous landscape is governed by this same structural property. The spatial problem, in effect, inherits its answer from the nonspatial one. This linkage is more than a mathematical curiosity—it provides a bridge between two literatures that have largely developed in parallel, allowing insights about competitive communities in single, well-mixed habitats to be translated into predictions about fragmented landscapes.</p>
<p>The landscape-size effect emerges naturally from this framework. When a landscape contains more patches, the total density term in the persistence balance grows, because a species has more opportunities to maintain individuals somewhere in the network. The local exclusion rate, by contrast, is a property of the patch and its immediate competitive environment. As the number of patches increases, the balance tips further toward persistence, and the range of conditions under which multiple species can coexist locally widens. This explains a pattern that field ecologists have documented repeatedly: larger habitat networks harbor more species per patch, not just more species in total. The mechanism is subtle—larger landscapes do not simply offer more habitat or more niches in this model; they buffer each local community against the stochastic and deterministic forces of exclusion by drawing on a larger regional pool of individuals.</p>
<p>Weak dispersal enters the picture because it is what allows this buffering to operate without destroying the heterogeneity that makes it valuable. When dispersal is weak, each patch retains much of its distinct character, and species can maintain different abundances in different places, exploiting the landscape as a mosaic of refuges and source areas. The total-density-versus-exclusion balance remains favorable because individuals produced in favorable patches can, slowly, subsidize populations in unfavorable ones. When dispersal becomes strong, the spatial structure effectively collapses: all patches converge toward similar compositions, the landscape behaves like a single well-mixed habitat, and the advantages of heterogeneity evaporate. The theory thus identifies weak dispersal not as a marginal condition but as the regime in which spatial coexistence mechanisms are strongest.</p>
<p>An important strength of the study is that the authors did not stop at approximation. They confronted their analytical predictions with numerical simulations of the full spatial Lotka–Volterra systems, exploring how the theory fares across gradients of dispersal rate and interaction strength. The verdict is largely reassuring: the approximations hold across most of the parameter space examined. The theory breaks down only in a narrow corner of parameter space where both dispersal and competitive interactions are very strong. In that regime, the effect of dispersal on coexistence becomes unimodal rather than monotonic—coexistence first improves and then declines as dispersal increases, producing the intermediate optimum familiar from earlier theoretical work. That this breakdown requires the joint presence of strong dispersal and strong competition is informative. It suggests that for the many natural systems where competitive interactions are moderate, the monotonic prediction—more dispersal is not better, but weak dispersal is reliably good—should hold.</p>
<p>The treatment of landscape size in the simulations is equally notable. Across the parameter regimes where an effect could be detected, landscape size retained a positive influence on coexistence without exception. Unlike dispersal, whose effect can flip sign under extreme conditions, the landscape-size effect proved robust. This asymmetry matters for conservation thinking, because it implies that enlarging or connecting habitat networks operates through a mechanism that does not depend on fine-tuned conditions. Adding patches to a network consistently expands the feasibility of local coexistence, whereas manipulating dispersal requires knowing where on the response curve a particular system sits.</p>
<p>The empirical component of the study gives these theoretical claims a grounding in the real world. The authors analyzed long-term data from a natural metacommunity of microcrustaceans, a group whose small size, rapid population dynamics, and occupancy of discrete habitat units make them classic subjects for metacommunity research. Two findings stand out. First, the data revealed strong competition among the species, confirming that the competitive assumptions of the models are appropriate for this system. Second, and more strikingly, the dispersal rate showed no detectable effect on local coexistence, while species co-occurrence increased with local landscape size, exactly as the theory predicts. In a field where dispersal is often assumed to be the dominant driver of local diversity patterns, this null result for dispersal—paired with a positive result for landscape size—is a pointed illustration of the theory&#8217;s central claim: in strongly competitive systems, the spatial architecture of the landscape, not the rate of movement through it, is what sustains local richness.</p>
<p>It is worth pausing on what this means for the interpretation of biodiversity patterns more broadly. Local species richness, the number of species coexisting at a single site, is shaped by processes operating at multiple scales: regional speciation and extinction, dispersal limitation, environmental filtering, and local species interactions. The new results do not deny this multiplicity, but they isolate one thread with unusual clarity. For communities governed by competition, the local coexistence of species is not primarily a consequence of how much individuals move, provided movement is weak, but of how much landscape is available for the metacommunity as a whole. This reframing shifts attention from corridors and connectivity—long the centerpiece of spatial conservation planning—toward the sheer extent and number of habitat patches, at least for competitive systems in heterogeneous environments.</p>
<p>The analytical link to the feasibility domain also opens a practical avenue for prediction. Feasibility is a property that can, in principle, be estimated from pairwise interaction coefficients and growth rates, quantities that ecologists can measure in controlled experiments or infer from time-series data. If local coexistence in a landscape is governed by the feasibility domain of the underlying competitive system, then measuring these parameters in one place may allow researchers to anticipate coexistence outcomes elsewhere, without needing to characterize every patch in detail. This is a meaningful step toward making spatial biodiversity theory operational rather than merely descriptive.</p>
<p>There are, of course, boundaries to what the study claims. The models assume competitive interactions as the organizing force, and the authors are careful to note that their conclusions concern competitive systems specifically. Communities structured instead by predation, mutualism, or facilitation may obey different rules, and the balance between total density and local exclusion may take different forms. Similarly, the microcrustacean system, while a valuable test case, represents one kind of natural metacommunity; whether the same landscape-size signature appears in systems with different dispersal modes, patch dynamics, or environmental drivers remains an open empirical question. The theory&#8217;s breakdown under jointly strong dispersal and strong competition also marks a region where future work is needed to characterize what actually happens when the approximations fail.</p>
<p>Nevertheless, the convergence of three lines of evidence—analytical approximation, numerical simulation, and long-term field data—gives the central result an unusually firm foundation. Weak dispersal promotes local species richness in heterogeneous competitive metacommunities, this promotion strengthens with landscape size, and both facts follow from a single structural principle linking spatial coexistence to the feasibility of the underlying competitive system. For a question that has persisted in spatial ecology for decades, the answer arrives with rare generality: the pattern ecologists kept observing in fragmented landscapes was never an accident of particular systems, but a predictable consequence of how competition, movement, and landscape geometry interact.</p>
<p><strong>Subject of Research:</strong> Spatial coexistence theory explaining how weak dispersal and landscape size promote local biodiversity in competitive metacommunities</p>
<p><strong>Article Title:</strong> Weak dispersal and landscape size inevitably promote local biodiversity in heterogeneous metacommunities of competing species</p>
<p><strong>Article References:</strong> De Laender, F., Gonzalez, A., Bleeckx, O., Ebert, D., &amp; Barabás, G. (2026). Weak dispersal and landscape size inevitably promote local biodiversity in heterogeneous metacommunities of competing species. <em>PLOS Computational Biology, 22</em>(10), e1014028. <a href="https://doi.org/10.1371/journal.pcbi.1014028" rel="noopener noreferrer">https://doi.org/10.1371/journal.pcbi.1014028</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.1371/journal.pcbi.1014028" rel="noopener noreferrer">10.1371/journal.pcbi.1014028</a></p>
<p><strong>Keywords:</strong> metacommunity, biodiversity, dispersal, species coexistence, Lotka-Volterra competition, landscape ecology, feasibility domain, spatial ecology, microcrustaceans, competitive exclusion, habitat patches, theoretical ecology</p>
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		<post-id xmlns="com-wordpress:feed-additions:1">289633</post-id>	</item>
		<item>
		<title>Galápagos Lava Lizards Shrink Their Territories When the Cool-Dry Season Sets In</title>
		<link>https://scienmag.com/galapagos-lava-lizards-shrink-their-territories-when-the-cool-dry-season-sets-in/</link>
		
		<dc:creator><![CDATA[Drew Townsend]]></dc:creator>
		<pubDate>Fri, 16 Oct 2026 04:47:18 +0000</pubDate>
				<category><![CDATA[Biology]]></category>
		<category><![CDATA[Science News]]></category>
		<category><![CDATA[adaptations of Galápagos reptiles to environmental fluctuations]]></category>
		<category><![CDATA[conservation insights from lizard seasonal behavior]]></category>
		<category><![CDATA[detailed tracking of Galápagos l]]></category>
		<category><![CDATA[ectotherm]]></category>
		<category><![CDATA[effects of temperature and water availability on lizard activity]]></category>
		<category><![CDATA[Galápagos]]></category>
		<category><![CDATA[Galápagos lava lizard behavior]]></category>
		<category><![CDATA[habitat selection]]></category>
		<category><![CDATA[home range]]></category>
		<category><![CDATA[impact of cool-dry season on tropical ectotherms]]></category>
		<category><![CDATA[lava lizard]]></category>
		<category><![CDATA[lizard territorial range reduction during dry season]]></category>
		<category><![CDATA[Microlophus bivittatus]]></category>
		<category><![CDATA[movement patterns of lava lizards]]></category>
		<category><![CDATA[radiotelemetry]]></category>
		<category><![CDATA[radiotelemetry study of San Cristóbal lizards]]></category>
		<category><![CDATA[reptile behavior]]></category>
		<category><![CDATA[San Cristóbal]]></category>
		<category><![CDATA[seasonal activity changes in reptiles]]></category>
		<category><![CDATA[seasonality]]></category>
		<category><![CDATA[spatial ecology]]></category>
		<category><![CDATA[spatial reorganization of reptiles in response to climate]]></category>
		<category><![CDATA[thermoregulation]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=281774</guid>

					<description><![CDATA[Radiotelemetry tracking of San Cristóbal lava lizards reveals that they shrink their activity areas by more than half and sometimes remain inactive for days during the cool-dry season, adjusting their habitat use to seasonal swings in temperature, water, and food availability.]]></description>
										<content:encoded><![CDATA[<p>On the rocky slopes of San Cristóbal in the Galápagos, the islands&#8217; most visible reptiles are quietly rewriting the rules of survival. A new radiotelemetry study of the San Cristóbal lava lizard (Microlophus bivittatus) reveals that these small, sun-loving animals dramatically compress their daily lives when the archipelago slides from its hot, wet season into the cool, dry one. Lizards tracked across both periods cut their activity areas by more than half, moved far shorter distances each day, and sometimes simply stopped moving altogether for days at a time. The findings offer one of the most detailed portraits yet of how a tropical ectotherm reorganizes its spatial world in response to seasonal swings in temperature, water, and food.</p>
<p>The research, published in Neotropical Biology and Conservation, followed radio-tagged lizards at a study site near Frigatebird Hill during March 2016, at the peak of the hot-wet season, and again in August 2016, during the cool-dry period. Researchers fitted each animal with a 0.5-gram radio transmitter glued to the dorsal pelvis, then relocated them three times a day, in the morning, at midday, and in the late afternoon. Over 165 total tracking days and 451 radiolocations, the team mapped each lizard&#8217;s movements on a 60-by-60-meter survey grid, then analyzed the resulting tracks with two complementary methods: minimum convex polygons, which enclose all recorded positions, and autocorrelated kernel density estimation, a statistical approach that captures clusters of repeated use within an animal&#8217;s range.</p>
<p>The seasonal contrast was stark. Lizards in March moved an average of 14.2 meters per day, while those in August managed only 5.8 meters, a large effect size that held regardless of sex. Activity areas told the same story. The mean core area, representing the 50 percent utilization distribution, shrank from roughly 151 square meters in March to just 43 square meters in August. Overall home ranges, measured as 95 percent utilization distributions, contracted from about 750 square meters to 238 square meters. These are not subtle shifts; they represent a fundamental restructuring of how much space an individual lizard needs to make a living depending on the time of year.</p>
<p>Equally striking was what the lizards did with the space they retained. Rather than wandering uniformly across their ranges, individuals concentrated their movements within a single core area, occasionally making repeated forays to specific peripheral spots. The researchers interpret these excursions as likely related to searching for prey, establishing ambush sites, or monitoring potential mates and rivals. When neighboring lizards&#8217; ranges overlapped, the overlap occurred almost exclusively at the broader 95 percent level. Core areas, by contrast, rarely overlapped at all, suggesting that these tightly used zones function as de facto territories within larger, more permissive activity areas.</p>
<p>Habitat selection proved equally season-dependent. In March, the strongest predictors of where a lizard chose to position itself were distance to the nearest low tree and substrate temperature. Lizards selected microhabitats with cooler substrate temperatures than random sites would predict, and they positioned themselves roughly 2.4 times farther from low trees than expected in the morning, gradually moving closer as the day progressed. This pattern is consistent with a classic thermoregulatory strategy: bask on open rock faces in the cool morning, then retreat to shaded spots as the equatorial sun climbs. By afternoon, lizards had shifted to rocks under canopy, detritus, and the vicinity of larger trees.</p>
<p>In August, the picture changed entirely. The top statistical models pointed toward rock crevices and open rock faces, but no single predictor received strong, consistent support across the model set. Lizards spent their days in or near crevices, on detritus, or under low vegetation, and four individuals, two females and two males, were documented remaining inactive for entire days. One male was stationary for six consecutive days, moved 11.4 meters in a single burst, then settled back into near-total inactivity. This kind of multi-day dormancy was essentially absent during the hot-wet period.</p>
<p>The researchers attribute these behavioral shifts to a combination of thermal and resource constraints. During March 2016, operative temperatures on open rock faces in direct sunlight exceeded the lizards&#8217; preferred body temperature range by roughly 8 degrees Celsius, making shaded rock faces under canopy the only viable midday option. In August, by contrast, temperatures in sun and shade converged and fell within the preferred range only briefly during late morning and early afternoon. Yet lizards still overwhelmingly chose shaded rock faces, possibly because conductive heat from rock surfaces remains available even under leafless canopy, or because staying hidden reduces exposure to predators such as Galápagos racers, hawks, and feral cats.</p>
<p>Resource scarcity likely compounds the thermal story. By August, the dominant palo santo and Jerusalem thorn trees had dropped most of their leaves, leaving primary production to sparse evergreen shrubs and grasses. Since lava lizards consume both plant material and arthropods, the cool-dry season represents a bottleneck in both food and water availability. Reduced movement and extended inactivity may be an energy-conservation strategy, similar to patterns documented in other tropical reptiles such as Guatemalan beaded lizards, which contract their home ranges by up to 90 percent during dry periods.</p>
<p>The study&#8217;s authors caution that their monitoring windows were relatively short, offering snapshots rather than a full annual picture. Still, the consistency of the seasonal effect across all measured metrics, from daily distance to home range size to microhabitat choice, suggests that San Cristóbal lava lizards are finely tuned to the temporal rhythm of their environment. As climate patterns shift and El Niño and La Niña events grow more variable, understanding how these lizards buffer themselves against seasonal extremes may become increasingly important for predicting their resilience across the Galápagos.</p>
<p>What emerges from this work is a portrait of an animal that is neither a passive hostage of its thermal environment nor a freewheeling explorer of its landscape. Instead, the San Cristóbal lava lizard operates as a strategic compromise artist, expanding its world when conditions permit and contracting it when they do not, always balancing the competing demands of staying warm enough, staying hydrated, staying fed, and staying alive.</p>
<p><strong>Subject of Research:</strong> Seasonal variation in spatial ecology, habitat use, and habitat selection of the San Cristóbal lava lizard in the Galápagos</p>
<p><strong>Article Title:</strong> Seasonal variations in spatial ecology, habitat use and habitat selection by San Cristóbal lava lizards Microlophus bivittatus in Galápagos</p>
<p><strong>Article References:</strong> Rowe, J. W., Moore, J. A., Fonley, M. R., Clark, D. L., &amp; Valle, C. A. (2026). Seasonal variations in spatial ecology, habitat use and habitat selection by San Cristóbal lava lizards Microlophus bivittatus in Galápagos. <em>Neotropical Biology and Conservation, 21</em>(2), 149-171. <a href="https://doi.org/10.3897/neotropical.21.e185618" rel="noopener noreferrer">https://doi.org/10.3897/neotropical.21.e185618</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.3897/neotropical.21.e185618" rel="noopener noreferrer">10.3897/neotropical.21.e185618</a></p>
<p><strong>Keywords:</strong> Galápagos, lava lizard, Microlophus bivittatus, radiotelemetry, habitat selection, thermoregulation, seasonality, home range, ectotherm, spatial ecology, San Cristóbal, reptile behavior</p>
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		<post-id xmlns="com-wordpress:feed-additions:1">281774</post-id>	</item>
		<item>
		<title>Trapdoor Spider Censuses Reveal 66,000 Hidden Burrows in California&#8217;s Vanishing Dunes</title>
		<link>https://scienmag.com/trapdoor-spider-censuses-reveal-66000-hidden-burrows-in-californias-vanishing-dunes/</link>
		
		<dc:creator><![CDATA[Margaret Porter]]></dc:creator>
		<pubDate>Thu, 15 Oct 2026 13:05:00 +0000</pubDate>
				<category><![CDATA[Science News]]></category>
		<category><![CDATA[Aptostichus stephencolberti]]></category>
		<category><![CDATA[arachnid research in California]]></category>
		<category><![CDATA[California coastal dune spiders]]></category>
		<category><![CDATA[California coastal dunes]]></category>
		<category><![CDATA[California dune habitat biodiversity]]></category>
		<category><![CDATA[coastal squeeze]]></category>
		<category><![CDATA[conservation]]></category>
		<category><![CDATA[desert and dune spider ecology]]></category>
		<category><![CDATA[distribution]]></category>
		<category><![CDATA[ecosystem engineers]]></category>
		<category><![CDATA[endangered coastal dune species]]></category>
		<category><![CDATA[endemic trapdoor spider species]]></category>
		<category><![CDATA[Frontiers in Arachnid Science]]></category>
		<category><![CDATA[hidden burrows of trapdoor spiders]]></category>
		<category><![CDATA[impact of habitat loss on trapdoor spiders]]></category>
		<category><![CDATA[mygalomorph spiders]]></category>
		<category><![CDATA[mygalomorph spiders in California]]></category>
		<category><![CDATA[population census]]></category>
		<category><![CDATA[scientific estimates of spider populations]]></category>
		<category><![CDATA[Spatial]]></category>
		<category><![CDATA[spatial ecology]]></category>
		<category><![CDATA[trapdoor spider conservation]]></category>
		<category><![CDATA[trapdoor spiders]]></category>
		<category><![CDATA[Trapdoor spiders population survey]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=274255</guid>

					<description><![CDATA[The first-ever population census of California's coastal dune trapdoor spiders estimates more than 66,000 individuals across two state beaches — and reveals that the same spiders follow completely different spatial rules at each site, with major implications for dune conservation.]]></description>
										<content:encoded><![CDATA[<p>Along California&#8217;s central coast, beneath the wind-scoured sand of two protected state beaches, tens of thousands of trapdoor spiders are quietly living out their lives behind camouflaged silk doors — and for the first time, scientists have counted them. A team led by M. Fran Keller of Folsom Lake College and Kylie Dickinson, Emma Jochim, Iris Quayle, Julianna Campos, Hanna Briggs, Colton Wiggins, and Jason Bond of the University of California, Davis, has published the first population estimation surveys for coastal dune trapdoor spiders anywhere in the world. Their study, appearing in Frontiers in Arachnid Science, estimates roughly 35,206 spiders at Sunset State Beach in Santa Cruz County and about 30,959 at Moss Landing State Beach in Monterey County — a combined hidden population of more than 66,000 individuals in habitats that together cover less than 200,000 square meters of dune sand.</p>
<p>The spiders in question are mygalomorphs, an ancient lineage of heavy-bodied, long-lived burrowing spiders that includes tarantulas and their relatives. Five species of trapdoor spider are known to be endemic to California&#8217;s coastal dunes: Aptostichus miwok, Aptostichus ramirezae, Aptostichus simus, Aptostichus stephencolberti, and Cryptocteniza kawtak. The last of these, described by Bond and colleagues in 2020 as an endangered living fossil along the Central Coast, underscores how precarious these relict populations are. Each spider constructs a silk-lined burrow capped with a hinged trapdoor, and each burrow is effectively a census unit: the team assumed one spider per occupied burrow, a reasonable assumption given that these spiders are solitary and territorial for most of their lives.</p>
<p>Counting animals that spend their entire lives underground presents an obvious methodological challenge, and the researchers solved it with a deceptively simple design. At each site, they mapped a long, thin sampling strip of roughly 26,000 square meters — 30 meters wide and hundreds of meters long — and overlaid it with a continuous grid of one-square-meter quadrats. From that grid, they randomly selected 150 plots per site using computer-generated random numbers, eliminating the human tendency to sample where burrows are easiest to find. Surveyors were trained to distinguish occupied burrows, identified by their thick, multilayered, bright white silk that remains elastic when handled, from abandoned burrows, whose silk turns gray to black, becomes fragile, and often loses its door entirely. This standardization matters because mygalomorphs are not the only silk-producers in the dunes, and misidentification would inflate the counts.</p>
<p>The raw numbers are striking. At Sunset State Beach, occupied burrow density came out at 0.287 burrows per square meter — about 29 trapdoor spiders per 100 square meters — which, extrapolated across roughly 121,406 square meters of potential habitat, yields the estimate of 35,206 spiders. Moss Landing was denser still: 0.453 burrows per square meter, or just over 45 spiders per 100 square meters, across approximately 68,797 square meters of habitat north of the jetty road, for an estimated 30,959 individuals. The single densest quadrat, at Moss Landing, contained 17 occupied burrows crammed into one square meter of sand. Remarkably, the mean number of occupied burrows did not differ significantly between the two sites, indicating that overall burrow densities were statistically similar even as the spatial stories behind those densities diverged dramatically.</p>
<p>And diverge they did. At Sunset State Beach, burrow presence was strongly and positively associated with vegetation. A Fisher&#8217;s exact test on the combined dataset found a significant relationship between plant presence and burrow presence, with an odds ratio of 6.29 — meaning a quadrat with plants was more than six times as likely to contain a burrow. A negative binomial model, chosen because burrow counts were overdispersed relative to the mean, confirmed that plant presence significantly predicted burrow abundance. Nearest-neighbor analysis drove the point home: quadrats with burrows sat an average of just 0.21 meters from the nearest plant, compared with 1.00 meters for quadrats without burrows, a difference confirmed by a Wilcoxon rank-sum test. The spiders at Sunset, in short, are building their homes in the shadow of dune plants — even though the vegetation itself was randomly distributed across the site.</p>
<p>At Moss Landing, the pattern inverted. No significant vegetation–burrow association was detected by any test: the Fisher&#8217;s exact odds ratio was a nonsignificant 1.37, the Spearman correlation between plant and burrow presence was essentially zero, and plant presence failed to predict burrow abundance in the negative binomial model. Yet burrows were still spatially clustered — Moran&#8217;s I, a measure of spatial autocorrelation, indicated significant positive clustering of burrow presence at both sites. The crucial difference is that at Moss Landing, the clustering of burrows was decoupled from the clustering of plants. Both burrows and vegetation were aggregated there, but the two aggregations did not overlap in any statistically meaningful way, and burrow-present quadrats were not significantly closer to vegetation than burrow-absent ones. Something other than plants is organizing the Moss Landing population.</p>
<p>The authors propose several ecological mechanisms for this contrast. At Sunset, where a single species, Aptostichus stephencolberti, appears to dominate, the strong vegetation association is consistent with an ideal free distribution, in which individuals preferentially occupy the best microhabitats — in this case, areas where plant roots may physically support burrow walls in loose aeolian sand. Dune plants also concentrate arthropod prey, including the tenebrionid dune beetle Coelus, which the team consistently found beneath plants and whose remains turned up inside trapdoor spider burrows. At Moss Landing, by contrast, the higher burrow density likely reflects a multi-species assemblage in which competition for space and resources, density-dependent processes, limited dispersal, and microclimate constraints shape where spiders settle. Juvenile burrows clustered near adult burrows suggest that spiderlings disperse only short distances from their mothers, a life-history trait that would generate spatial clustering independent of any plant cue.</p>
<p>The timing of the surveys adds an important caveat to the population estimates. The counts were conducted in July and August, precisely when male trapdoor spiders abandon their burrows to wander in search of mates — and when other studies of mygalomorph populations have documented dramatic seasonal swings in burrow density, from as low as 0.01 to 0.19 individuals per square meter within a single summer. Maternal care complicates the picture further: the team found large female burrows where females and up to 200 spiderlings retreated to the deepest chambers when disturbed, and related work on the dune-obligate wolf spider Geolycosa wrightii has shown that females temporarily seal their burrows during brooding, making active burrows harder to detect. The true populations may fluctuate considerably across the year, and the estimates should be read as seasonal snapshots rather than permanent censuses.</p>
<p>What makes the study genuinely consequential is its conservation message: the same species, living in the same kind of habitat, obeys different spatial rules at different sites. At Sunset, where vegetation predicts both burrow occurrence and abundance, trampling, invasive species, or coastal development that strips plant cover could disproportionately destroy habitat suitability — making native dune vegetation restoration a direct investment in spider conservation. At Moss Landing, where burrow density is higher but vegetation is irrelevant to burrow placement, the priority shifts to protecting the physical integrity and contiguity of the dune system itself, preserving soil stability, microclimate, and the spatial structure that density-dependent processes have built. A one-size-fits-all dune management plan, the authors argue, would fail both populations.</p>
<p>The broader stakes are considerable. California&#8217;s 3,427 miles of coastline once supported vast, continuous dune systems, but decades of agricultural, residential, and commercial development have fragmented them into disjunct islands — a process of coastal squeeze that traps endemic dune species between the rising Pacific and the hardened terrestrial back beach. Trapdoor spiders are poor dispersers with restricted gene flow, long life spans, and extreme habitat specificity, exactly the profile that pushes habitat specialists from vulnerable to extinction. Yet dune conservation has historically fixated on charismatic umbrella species — snowy plovers, dune plants, butterflies — while burrowing arthropods like Aptostichus stephencolberti have been assumed to benefit passively from protections timed around bird nesting seasons and plant blooming periods. Those closures rarely coincide with the July and August mating wanderings of male spiders, leaving dispersing juveniles exposed when beaches reopen and visitors slide down dune faces, crushing burrows and burying their doors. If these spiders are, as the spatial evidence suggests, ecosystem engineers whose burrows alter soil aeration, moisture retention, and sediment stability — and if shorebirds increasingly depend on dune invertebrates as sea level rise erodes intertidal foraging grounds — then the unseen 66,000 spiders of Sunset and Moss Landing may be holding up far more of the dune ecosystem than their numbers alone imply. Baseline censuses like this one are the first step toward noticing them before they are gone.</p>
<p><strong>Subject of Research:</strong> trapdoor spiders</p>
<p><strong>Article Title:</strong> The distribution, spatial clustering, and density of trapdoor spiders in two California coastal dune ecosystems</p>
<p><strong>Article References:</strong> Keller, M. F., Dickinson, K. A., Jochim, E. E., Quayle, I. L., Campos, J. E., Briggs, H. R., Wiggins, C. R., &amp; Bond, J. E. (2026). The distribution, spatial clustering, and density of trapdoor spiders in two California coastal dune ecosystems. <em>Frontiers in Arachnid Science, 5</em>, Article 1913353. <a href="https://doi.org/10.3389/frchs.2026.1913353" rel="noopener noreferrer">https://doi.org/10.3389/frchs.2026.1913353</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.3389/frchs.2026.1913353" rel="noopener noreferrer">10.3389/frchs.2026.1913353</a></p>
<p><strong>Keywords:</strong> trapdoor spiders, California coastal dunes, mygalomorph spiders, population census, spatial ecology, conservation, Aptostichus stephencolberti, ecosystem engineers, coastal squeeze, Frontiers in Arachnid Science, distribution, spatial</p>
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		<post-id xmlns="com-wordpress:feed-additions:1">274255</post-id>	</item>
		<item>
		<title>Rare Species May Be Safer Than They Look: Dispersal Diversity Shields Forests From Extinction</title>
		<link>https://scienmag.com/rare-species-may-be-safer-than-they-look-dispersal-diversity-shields-forests-from-extinction/</link>
		
		<dc:creator><![CDATA[Margaret Porter]]></dc:creator>
		<pubDate>Fri, 09 Oct 2026 12:01:22 +0000</pubDate>
				<category><![CDATA[Biology]]></category>
		<category><![CDATA[biodiversity]]></category>
		<category><![CDATA[biodiversity and ecosystem stability]]></category>
		<category><![CDATA[coexistence]]></category>
		<category><![CDATA[community dynamics and species coexistence]]></category>
		<category><![CDATA[community ecology]]></category>
		<category><![CDATA[competitive exclusion]]></category>
		<category><![CDATA[competitive exclusion in species communities]]></category>
		<category><![CDATA[conservation]]></category>
		<category><![CDATA[conservation biology and rare species protection]]></category>
		<category><![CDATA[dispersal]]></category>
		<category><![CDATA[dispersal kernels and species persistence]]></category>
		<category><![CDATA[Dispersal strategy diversity in forest ecosystems]]></category>
		<category><![CDATA[dynamical mean-field theory]]></category>
		<category><![CDATA[ecological buffers against extinction]]></category>
		<category><![CDATA[ecological resilience and species survival]]></category>
		<category><![CDATA[forest plots]]></category>
		<category><![CDATA[mathematical modeling in ecology]]></category>
		<category><![CDATA[metacommunity]]></category>
		<category><![CDATA[metapopulation capacity and extinction risk]]></category>
		<category><![CDATA[physics-inspired ecological frameworks]]></category>
		<category><![CDATA[spatial ecology]]></category>
		<category><![CDATA[species dispersal mechanisms and local extinction prevention]]></category>
		<category><![CDATA[species vulnerability]]></category>
		<category><![CDATA[statistical physics]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=253697</guid>

					<description><![CDATA[A statistical-physics framework applied to three forest censuses shows that dispersal diversity, rather than abundance alone, buffers species against competitive exclusion and local extinction.]]></description>
										<content:encoded><![CDATA[<p>One of the most stubborn puzzles in ecology is deciding which species are truly on the brink. Conservation biologists have long leaned on abundance as the default alarm bell: if a species is rare, it must be at risk. But a new study published in Nature Ecology &amp; Evolution argues that this intuition is only half the story. By importing mathematical tools from the physics of disordered systems, a team led by Davide Bernardi of the University of Padova, together with collaborators including Simon Levin of Princeton University and Andrea Rinaldo of EPFL, has built a framework that measures how close each species in a community sits to competitive exclusion—and found that the diversity of dispersal strategies, not sheer numbers, is what buffers many species against local extinction.</p>
<p>The core of the work is a single, measurable quantity the authors call the competitive balance. In classic metapopulation theory, a species persists when its local extinction rate is lower than the so-called metapopulation capacity, typically captured by the largest eigenvalue of a dispersal kernel matrix. That logic works for a lone species, but in a community of many competitors, meeting the threshold is necessary yet not sufficient. The new framework shows that long-term persistence in an interacting metacommunity is instead governed by how a species&#8217; competitive balance compares with those of all its neighbors—a collective property that emerges nonlinearly from the whole community rather than summing individual contributions.</p>
<p>What makes the approach practical is its refusal to demand data that ecologists rarely have. Mechanistic models of interacting communities usually require estimates of demographic rates, interaction coefficients and dispersal parameters, which are notoriously difficult to measure in species-rich ecosystems. Statistical tools such as species distribution models or population viability analyses are more data-friendly but often treat species in isolation. The Padova-led team sidestepped the problem by modeling the interaction–dispersal kernel entries as effectively random, drawn from a species-specific gamma distribution whose parameters can be inferred directly from spatial abundance patterns—the kind of coarse-grained census data that forest monitoring plots already collect.</p>
<p>The bridge between theory and data is a quantity called the vacancy-adjusted abundance, or VAA. For each species in a subplot, the VAA is the fraction of space it occupies divided by the locally unoccupied space. This normalization upweights patches that are nearly saturated, so the same relative space-use contributes differently depending on how crowded a site is. The result has a clear ecological reading: it rescales local occupancy to reflect a species&#8217; effective colonization effort. Fitting the theoretical VAA distributions to empirical histograms yields two interpretable parameters per species—dispersal heterogeneity and effective dispersal strength—without any direct measurement of vital rates or interaction coefficients.</p>
<p>To validate the framework, the researchers turned to three spatially complete forest censuses: the Barro Colorado Island tropical plot in Panama, the Pasoh Forest Reserve plot in Malaysia and the Michigan Big Woods temperate plot in the United States. Each plot was partitioned into 50-meter square subplots, and the space used by each species was estimated using an established allometric relation between trunk diameter and crown area. The theory captured the diversity of distributional shapes across species with striking accuracy. In out-of-sample tests, parameters fitted on one half of a plot predicted the mean space-use of species in the other half with coefficients of determination of 0.97, 0.93 and 0.95 for the three datasets respectively.</p>
<p>The framework also outperformed ecological null models. Against a neutral negative-binomial model with community-level parameters, and against a species-specific variant matched in parameter count, the new theory achieved absolute goodness-of-fit consistent with a correctly specified model across all three forests, and beat the alternatives in relative comparisons. Perhaps most tellingly, the fitted parameters carried real biological signal: in the Barro Colorado Island data, gap-exploiting and intermediate tree species showed significantly higher dispersal heterogeneity than shade-tolerant species, consistent with the episodic local dominance that light-demanding trees achieve when canopy gaps open. Effective dispersal strength, by contrast, did not differ significantly between guilds.</p>
<p>The deeper payoff comes when the competitive balances of all species are computed from the fitted parameters. Although dispersal-related parameters varied widely among species in all three forests, the competitive balances themselves were tightly clustered around their mean. The theory predicts exactly this: a group of competing species can coexist as long as their balances are not too dissimilar, with full coexistence possible only within a limited region of balance space surrounding the equal-balance condition. Equal balance does not mean identical traits—simulations with species sharing the same balance but different dispersal strategies produced distinct abundances—so the narrow clustering reflects a community-wide trade-off rather than trait uniformity.</p>
<p>From this clustering, the team derived a vulnerability index: the distance between a community&#8217;s position in competitive-balance space and the critical boundary below which a given species cannot persist. A negative value signals persistence; a positive value means eventual competitive exclusion. Applied to the three forests, every analysed species fell safely below its threshold. More provocative was what the index revealed about rarity. Abundance and vulnerability were strongly correlated only near the extinction threshold; far from it, species with low average abundance were not necessarily in danger of competitive suppression. In simulations, species with positive vulnerabilities saw their stationary abundance collapse toward zero, but away from the threshold, abundances spread across a wide range, confirming that being rare does not automatically mean being doomed.</p>
<p>The explanation lies in spatial strategy. Holding mean abundance constant, the researchers found a significant negative partial correlation between the spatial heterogeneity of a species&#8217; space-use distribution and its vulnerability across all three datasets. Two Barro Colorado species made the point vividly: Prioria copaifera and Pterocarpus rohrii differ in total stem count by only about two percent, yet the former&#8217;s much more heterogeneous spatial distribution gives it a lower vulnerability. Intuitively, a heterogeneous dispersal strategy lets a species carve out spatial niches where it is hard to displace, trading some overall abundance for local strongholds. This trade-off between abundance, its spatial variability and vulnerability may be a key mechanism sustaining the coexistence of many species in the same forest.</p>
<p>The authors are careful about limits. The vulnerability index predicts final outcomes, not the timescales over which species approach them, and transient dynamics varied substantially in simulations. At very low abundances, demographic randomness will matter, and the framework cannot disentangle local competition from facilitation, both of which are folded into the inferred kernel parameters. Still, the applications are tantalizing: the same machinery could probe how an invasive species with a particular competitive balance might reconfigure a community, or whether suppressing a single species would trigger cascading exclusions like dominoes. An open-source package, vulntool, implements the core calculations. For a field racing to anticipate a potential mass extinction, the message is quietly radical: to know which species are truly at risk, look not just at how many individuals remain, but at how variedly they spread themselves across the landscape.</p>
<p><strong>Subject of Research:</strong> A statistical-physics framework quantifying species vulnerability to competitive exclusion in metacommunities using spatial abundance data</p>
<p><strong>Article Title:</strong> Dispersal diversity buffers species vulnerability to local extinction</p>
<p><strong>Article References:</strong> Bernardi, D., Nicoletti, G., Padmanabha, P., Suweis, S., Azaele, S., Levin, S. A., Rinaldo, A., &amp; Maritan, A. (2026). Dispersal diversity buffers species vulnerability to local extinction. <em>Nature Ecology &amp;amp; Evolution</em>. <a href="https://doi.org/10.1038/s41559-026-03195-y" rel="noopener noreferrer">https://doi.org/10.1038/s41559-026-03195-y</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.1038/s41559-026-03195-y" rel="noopener noreferrer">10.1038/s41559-026-03195-y</a></p>
<p><strong>Keywords:</strong> community ecology, metacommunity, dispersal, competitive exclusion, species vulnerability, coexistence, statistical physics, forest plots, biodiversity, spatial ecology, dynamical mean-field theory, conservation</p>
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		<post-id xmlns="com-wordpress:feed-additions:1">253697</post-id>	</item>
		<item>
		<title>Dunes Follow a Hidden Physics: Young Coastal Dune Landscapes Self-Organize Like Phase-Separating Fluids</title>
		<link>https://scienmag.com/dunes-follow-a-hidden-physics-young-coastal-dune-landscapes-self-organize-like-phase-separating-fluids/</link>
		
		<dc:creator><![CDATA[Katie Riggs]]></dc:creator>
		<pubDate>Mon, 05 Oct 2026 23:39:46 +0000</pubDate>
				<category><![CDATA[Chemistry]]></category>
		<category><![CDATA[building with nature]]></category>
		<category><![CDATA[building with nature strategies]]></category>
		<category><![CDATA[coastal dune formation]]></category>
		<category><![CDATA[coastal dunes]]></category>
		<category><![CDATA[coastal management]]></category>
		<category><![CDATA[coastal management and climate change adaptation]]></category>
		<category><![CDATA[dune landscape evolution]]></category>
		<category><![CDATA[ecology of marram grass and sand]]></category>
		<category><![CDATA[emergent patterns in coastal environments]]></category>
		<category><![CDATA[marram grass]]></category>
		<category><![CDATA[natural shoreline protection]]></category>
		<category><![CDATA[NIOZ]]></category>
		<category><![CDATA[phase separation]]></category>
		<category><![CDATA[phase separation in natural systems]]></category>
		<category><![CDATA[physical modeling of dune dynamics]]></category>
		<category><![CDATA[physics of sand and wind interactions]]></category>
		<category><![CDATA[PNAS]]></category>
		<category><![CDATA[sea level rise]]></category>
		<category><![CDATA[self-organization]]></category>
		<category><![CDATA[self-organization of dune landscapes]]></category>
		<category><![CDATA[spatial ecology]]></category>
		<category><![CDATA[tipping points]]></category>
		<category><![CDATA[universal principles in self-organizing systems]]></category>
		<category><![CDATA[Utrecht University]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=239594</guid>

					<description><![CDATA[New research shows that young coastal dune landscapes self-organize through phase-separation physics, revealing local tipping points beyond which damage to marram grass and sand patterns never heals.]]></description>
										<content:encoded><![CDATA[<p>Along the Dutch coast, the battle against rising seas is increasingly fought not with concrete but with sand, wind, and grass. The concept is known as building with nature: rather than imposing rigid engineering on the shoreline, coastal managers harness the natural processes that already shape it, allowing dunes to grow, shift, and shield the land behind them. But hitching a ride on natural processes only works if those processes are genuinely understood. Now, new research from the Netherlands reveals that young dune landscapes are not the random accumulations of sand they might appear to be. Instead, they behave as self-organizing systems whose architecture follows a precise and surprisingly universal physical principle, one that scientists can recognize in salad dressing as easily as on a windswept beach.</p>
<p>The study, published in the Proceedings of the National Academy of Sciences, was led by ecologist Paul Berghuis, who is affiliated with Utrecht University and the Royal Netherlands Institute for Sea Research, known as NIOZ. Berghuis specializes in spatial ecology, a field concerned with the patterns that emerge from the interplay between organisms and their environment. His subject was the relationship between marram grass and sand, a pairing long known to be central to dune formation. Marram grass traps windblown sand around its stems, and over years the trapped sand accumulates into the embryonic dunes that eventually grow into the protective barriers shielding much of the Dutch coastline. What Berghuis set out to determine was not how a single plant builds a single dune, but how thousands of plants and dozens of dunes interlock into a coherent landscape.</p>
<p>To answer that question, Berghuis turned to a source of information that spans decades: aerial photographs. By analyzing these images through time, he searched for fixed patterns in the way young dune landscapes arrange themselves. The approach deliberately shifted the scale of inquiry. As Berghuis explains, quite a lot is already known about individual plants and the processes acting on them, but the deeper question concerns how the complex system of sand and vegetation fits together as a whole. That question dictated the scale at which the dunes were studied. Rather than treating the landscape as a collection of individually operating grasses and dunes, he examined it as a system that organizes itself at the landscape level. Seen that way, he found, the dune landscape displays characteristics of growth and resilience that cannot be predicted from the behavior of individual dunes or grasses alone.</p>
<p>The first surprise was what the patterns were not. In previously studied ecosystems that self-organize, such as mussel beds or the patchy vegetation of savannas, a regular arrangement typically emerges: spots of roughly the same size, spaced at roughly the same distances, repeating across the landscape like a biological wallpaper. Dune landscapes break that rule. Berghuis discovered that there is no fixed size to the dune bodies at all. The reason lies in the restless nature of sand. Wind moves grains again and again before they finally settle somewhere, and the places where they settle are not chosen at random. Where marram grass plants grow closely together, the sand is retained most effectively. At these high densities of vegetation, a dune continues to grow, and it often does so at the expense of its neighbors. Small dunes are left behind or disappear entirely, while larger dunes merge together into ever bigger bodies.</p>
<p>That behavior, in which large units grow while small ones shrink and vanish, is the signature of a well-known physical process called phase separation. Co-author Koen Siteur and other colleagues had previously argued that the spatial organization of certain ecosystems resembles this physics, and the dune findings confirm the analogy with striking precision. Phase separation is familiar from the kitchen: when oil and vinegar are shaken together to make salad dressing, the oil first disperses into countless small droplets suspended in the vinegar. Left to stand, however, the droplets coalesce. Large droplets grow at the expense of small ones, because the physics of the interface between oil and vinegar favors consolidation. The same logic, the researchers found, governs sand and marram grass. Densely vegetated dunes capture sand more efficiently, drawing it away from sparsely vegetated neighbors, so the landscape coarsens over time much as the oil in a dressing does.</p>
<p>Crucially, the resemblance is not merely visual. Siteur&#8217;s theory, developed in earlier work, describes how phase-separating systems can be recognized by a very specific fingerprint in their statistics, and Berghuis reports that the dunes carry exactly that fingerprint. The distribution of dune sizes, the way in which dunes merge with one another, and even the rate at which the merging slows down over time all match what the theory of phase separation predicts. This is a significant scientific advance, because it moves the field from description to explanation. As Berghuis puts it, the researchers now know not only how dunes behave but also why they do so. A landscape that once seemed to be the idiosyncratic product of local wind and plant conditions is revealed to obey a general physical law, placing coastal dunes in the same theoretical family as droplets, alloys, and other systems that separate into distinct phases.</p>
<p>The practical consequences of that insight are considerable, because the theory does more than describe patterns; it makes predictions about how such systems respond to disturbance. According to the theory, damage to the spatial pattern does not heal itself once it exceeds a critical threshold. In a dune landscape, this could happen when marram grass is disturbed by trampling, or when wind scours a small pit in the sand. Intuition might suggest that such wounds would gradually fill in and recover, as many ecosystems do. The theory says otherwise. The disturbances are not repaired; instead, the sand that would be needed to heal them migrates away to the more densely vegetated dunes elsewhere in the landscape, reinforcing the winners and abandoning the losers. Local damage, in other words, can become permanent even while the system as a whole appears healthy.</p>
<p>Berghuis&#8217;s measurements show exactly such a threshold value in the amount of marram grass present. Below a certain vegetation density, the self-repair mechanisms of the dune system fail, and degradation becomes self-perpetuating. At the same time, the theory predicts that the system as a whole remains resilient in a particular sense: the sand is not lost from the landscape but merely redistributed, flowing from damaged or sparse areas toward the densely vegetated dunes that continue to grow. This dual character, locally fragile but globally stable, is precisely the kind of behavior that phase-separation theory is built to capture, and it fundamentally changes how coastal managers should interpret the landscapes they oversee. A dune area can look robust in aggregate while individual dunes, once pushed past their local tipping point, never recover.</p>
<p>For the philosophy of building with nature, these findings arrive at an opportune moment. As sea levels rise, the Netherlands and other coastal nations are betting increasingly on natural dune growth as a flexible, self-reinforcing line of defense, one that can keep pace with changing conditions in ways that fixed structures cannot. But that bet depends on knowing where the system&#8217;s limits lie. The new research supplies a quantitative answer: local damage can be permanent once vegetation density falls below a critical threshold, even if the dune area as a whole remains healthy, so management must attend to the fine-grained pattern of grass cover and sand, not merely to the total volume of the dune field. For anyone who wants to build with nature rather than against it, Berghuis argues, insights of this kind are crucial. The dunes, it turns out, have been organizing themselves all along according to rules written in physics, and learning to read those rules may determine how well the coast weathers the century ahead.</p>
<p><strong>Subject of Research:</strong> Spatial self-organization and phase-separation dynamics in coastal dune formation</p>
<p><strong>Article Title:</strong> Local tipping points in dune landscapes: how does a dune system organize itself?</p>
<p><strong>Article References:</strong> Local tipping points in dune landscapes: how does a dune system organize itself?. (n.d.). <a href="https://www.eurekalert.org/news-releases/1146342" rel="noopener noreferrer">Original publication</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> Not provided</p>
<p><strong>Keywords:</strong> coastal dunes, marram grass, self-organization, phase separation, spatial ecology, tipping points, coastal management, building with nature, Utrecht University, NIOZ, PNAS, sea level rise</p>
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