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	<title>tropical forest &#8211; Science</title>
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	<title>tropical forest &#8211; Science</title>
	<link>https://scienmag.com</link>
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		<title>Ancient Warm Period Reveals the Hidden Forces Behind India&#8217;s Monsoon Swings</title>
		<link>https://scienmag.com/ancient-warm-period-reveals-the-hidden-forces-behind-indias-monsoon-swings/</link>
		
		<dc:creator><![CDATA[Sloane Callahan]]></dc:creator>
		<pubDate>Fri, 09 Oct 2026 09:21:39 +0000</pubDate>
				<category><![CDATA[Climate]]></category>
		<category><![CDATA[AMOC]]></category>
		<category><![CDATA[Ancient climate variability]]></category>
		<category><![CDATA[Bay of Bengal]]></category>
		<category><![CDATA[Bay of Bengal seafloor sediment analysis]]></category>
		<category><![CDATA[carbon dioxide]]></category>
		<category><![CDATA[impact of past warm periods on monsoon patterns]]></category>
		<category><![CDATA[Indian monsoon history]]></category>
		<category><![CDATA[Indian summer monsoon]]></category>
		<category><![CDATA[influence of global warming on monsoon stability]]></category>
		<category><![CDATA[insolation]]></category>
		<category><![CDATA[interglacial]]></category>
		<category><![CDATA[interglacial periods and their relevance to modern climate]]></category>
		<category><![CDATA[Intertropical Convergence Zone]]></category>
		<category><![CDATA[IODP Site U1446]]></category>
		<category><![CDATA[long-term climate change and ecosystem shifts]]></category>
		<category><![CDATA[Marine Isotope Stage 11 climate reconstruction]]></category>
		<category><![CDATA[MIS 11]]></category>
		<category><![CDATA[paleoclimate]]></category>
		<category><![CDATA[paleoclimate insights for future monsoon prediction]]></category>
		<category><![CDATA[paleoclimatology and monsoon fluctuations]]></category>
		<category><![CDATA[pollen analysis]]></category>
		<category><![CDATA[role of orbital configurations in monsoon variability]]></category>
		<category><![CDATA[tropical forest]]></category>
		<category><![CDATA[tropical forest collapse and recovery]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=252985</guid>

					<description><![CDATA[A 400,000-year-old pollen record from the Bay of Bengal shows that India's monsoon and tropical forests swung dramatically during a warm interglacial resembling our own, with insolation dominating in warm phases and ice sheets and carbon dioxide taking over as glaciers grew.]]></description>
										<content:encoded><![CDATA[<p>Some 400,000 years ago, the Indian subcontinent was cloaked in lush tropical forest, sustained by a summer monsoon far stronger than anything the region experiences today. Then, in a matter of roughly 1,600 years, that forest collapsed by more than 20 percentage points, replaced by grasses and drought-tolerant shrubs, before rebounding just as dramatically. This extraordinary episode, buried in seafloor mud from the Bay of Bengal, is now telling scientists something unsettling about the future: even under globally warm conditions remarkably similar to our own, the monsoon can fail catastrophically.</p>
<p>The discovery comes from a new study published in the journal Climate of the Past, in which an international team of researchers led by Dulce Oliveira of the University of the Algarve and the University of Bordeaux reconstructed vegetation and monsoon variability across Marine Isotope Stage 11, or MIS 11, an interglacial period spanning roughly 426,000 to 374,000 years ago. MIS 11 has long fascinated paleoclimatologists because its orbital configuration resembles that of the Holocene, the current interglacial, and because it combined prolonged carbon dioxide-driven warming, higher-than-present sea levels linked to polar ice-sheet loss, and an unusually long duration. If scientists want a preview of how tropical ecosystems and the Indian summer monsoon might behave in a warmer world, MIS 11 is one of the best natural laboratories available.</p>
<p>To read that ancient landscape, the team turned to pollen grains preserved in sediments from IODP Site U1446, a core drilled during Expedition 353 on the northeastern Indian margin, offshore the Mahanadi River basin. The site was strategically positioned to capture rainfall signals from India&#8217;s Core Monsoon Zone, the central belt of the peninsula that receives 80 to 90 percent of its annual rainfall during the summer monsoon months of June through September. Because the narrow continental shelf near the river mouth efficiently delivers terrestrial material to the deep sea, the pollen extracted from the marine sediments provides an integrated picture of the vegetation across the watershed, from semi-evergreen coastal forests to dry deciduous savannas. The researchers analyzed 62 samples spanning late MIS 12 through early MIS 10, achieving an average temporal resolution of about 1,200 years, and grouped the pollen into ecologically meaningful categories, with moisture-loving wet evergreen forest taxa such as Elaeocarpus, Gnetum, Mallotus and Syzygium serving as the primary indicator of monsoon rainfall intensity.</p>
<p>The record reveals a striking transformation at the MIS 12 to MIS 11 transition. Semi-arid steppe, dominated by grasses and xerophytic plants like Amaranthaceae, gave way to tropical forest as the percentage of arboreal taxa surged from about 2 percent to 58 percent, a response the authors attribute to a steep northward shift of the Intertropical Convergence Zone and a rapid intensification of monsoon rainfall. During the interglacial substage MIS 11c, wet evergreen forest flourished for roughly 32,000 years, peaking around 414,000 to 407,000 years ago, when the monsoon reached its maximum intensity. Notably, the forest record follows an asymmetric M-shaped pattern with two peaks, mirroring similar structures seen in Antarctic methane concentrations and southern European pollen sequences, suggesting that shifts in the ITCZ&#8217;s mean position linked low- and mid-latitude hydroclimate and left a common imprint on tropical wetland methane emissions.</p>
<p>But the most dramatic moment in the record is not an expansion. Around 406,000 years ago, at the height of full interglacial conditions, the tropical forest abruptly contracted by 22.3 percentage points in roughly 1,600 years, with no subsequent recovery to previous levels during the optimum. The researchers link this event, labeled Fe-1, to a millennial-scale weakening of the summer monsoon, and they note a striking parallel: an abrupt cold and dry event of the same age is documented in marine pollen records off southern Europe, where it similarly terminated the interglacial optimum. Because the event occurred when ice volume was low and carbon dioxide concentrations were high and stable, the authors propose that a prolonged or more frequent El Niño-like state, possibly connected to North Atlantic circulation changes, may have weakened the monsoon and desiccated both regions simultaneously.</p>
<p>The second half of MIS 11 tells a different story. As ice sheets grew and atmospheric carbon dioxide declined during substages MIS 11b and MIS 11a, the forest record diverged from insolation trends and instead tracked carbon dioxide and sea-level reconstructions. Three further abrupt forest contractions, centered near 387,700, 383,300 and 374,600 years ago, coincide within dating uncertainties with North Atlantic cooling events and disruptions of the Atlantic meridional overturning circulation, the great ocean conveyor that redistributes heat across the hemispheres. The mechanism is well understood from younger records: when massive ice sheets discharged icebergs into the North Atlantic, the overturning circulation weakened, the ITCZ shifted southward, and the Indian summer monsoon faltered. Each contraction was rapidly followed, within 600 to 1,000 years, by a sharp forest rebound, coinciding with Dansgaard-Oeschger-like warming events, abrupt carbon dioxide jumps and methane overshoots recorded in Antarctic ice, all pointing to a sudden reinvigoration of ocean circulation and a poleward ITCZ shift that swelled tropical wetlands.</p>
<p>To disentangle the competing drivers, the team compared their pollen record with transient climate simulations performed with the LOVECLIM Earth system model, run with time-varying insolation and carbon dioxide over two precessional cycles. The comparison confirmed that during MIS 11c, the pattern and amplitude of the wet evergreen forest closely tracked precession-paced boreal summer insolation, peaking nearly in phase with the strongest insolation maximum while carbon dioxide remained high and sea level continued to rise. In warm climates with elevated carbon dioxide and reduced ice volume, insolation is the dominant control on the monsoon, acting through the thermal contrast between the Indian peninsula and the equatorial Indian Ocean. Conversely, during the glacial inception, expanding ice sheets and falling carbon dioxide overshadowed insolation, favoring carbon-hungry C4 grasses and reducing atmospheric moisture transport to the peninsula. The mismatch between data and model during late MIS 11, where the simulations continued to follow insolation, highlights a critical gap: models lacking dynamic ice sheets cannot capture the millennial-scale variability that dominated the record during that interval.</p>
<p>The findings carry a pointed message for the twenty-first century. Projections consistently indicate an intensifying Indian summer monsoon under continued warming, with the potential for denser vegetation and deciduous trees replacing grasslands across the peninsula. The MIS 11 simulations suggest that central India was considerably wetter and more forested at that interglacial&#8217;s climate optimum than during the pre-industrial period, thanks to much higher boreal summer insolation, offering a possible analogue for the greening expected under future scenarios. Yet the abrupt forest collapse at 406,000 years ago demonstrates that extreme monsoon weakening can strike even under globally warm, high-carbon-dioxide conditions, precisely the state the planet is entering now. The tropical forests of India are a key component of both the global carbon and methane cycles, and their sensitivity to sudden hydroclimatic shocks has now been demonstrated for a warm world.</p>
<p>What makes the study especially significant is that it fills a long-standing gap in the monsoon archive. While East Asian summer monsoon variability during MIS 11 has been documented in Chinese speleothems, records from India&#8217;s Core Monsoon Zone older than the Holocene were previously limited to lower-resolution marine sequences focused on glacial-interglacial cycles. By resolving millennial-scale events within a single interglacial, the Site U1446 pollen record shows that the Indian and East Asian monsoon subsystems responded heterogeneously to the same forcings, and that neither a purely insolation-driven nor a purely ice-volume-driven explanation suffices. Instead, the dominant control shifts with the baseline climate state, and abrupt, high-latitude-triggered events can override the orbital pacemaker altogether. As the authors note, future research should prioritize the atmospheric circulation patterns, particularly El Niño-like dynamics, that can synchronize drought across low and mid-latitudes, because understanding those teleconnections may prove essential for anticipating how the monsoon and the forests it sustains will behave as the planet continues to warm.</p>
<p><strong>Subject of Research:</strong> Indian summer monsoon and tropical vegetation variability during Marine Isotope Stage 11</p>
<p><strong>Article Title:</strong> Complex interplay of forcings drives Indian vegetation and summer monsoon variability during MIS 11</p>
<p><strong>Article References:</strong> Oliveira, D., Desprat, S., Yin, Q., Zorzi, C., Wu, Z., Anupama, K., Prasad, S., Alonso-García, M., &amp; Martinez, P. (2026). Complex interplay of forcings drives Indian vegetation and summer monsoon variability during MIS 11. <em>Climate of the Past, 22</em>(9), 1691-1709. <a href="https://doi.org/10.5194/cp-22-1691-2026" rel="noopener noreferrer">https://doi.org/10.5194/cp-22-1691-2026</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.5194/cp-22-1691-2026" rel="noopener noreferrer">10.5194/cp-22-1691-2026</a></p>
<p><strong>Keywords:</strong> Indian summer monsoon, MIS 11, paleoclimate, pollen analysis, IODP Site U1446, Intertropical Convergence Zone, tropical forest, AMOC, insolation, carbon dioxide, Bay of Bengal, interglacial</p>
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		<post-id xmlns="com-wordpress:feed-additions:1">252985</post-id>	</item>
		<item>
		<title>New QGIS Plugin Brings NASA&#8217;s Space Laser Forest Data to Everyone</title>
		<link>https://scienmag.com/new-qgis-plugin-brings-nasas-space-laser-forest-data-to-everyone/</link>
		
		<dc:creator><![CDATA[Violet Maxwell]]></dc:creator>
		<pubDate>Thu, 08 Oct 2026 08:25:46 +0000</pubDate>
				<category><![CDATA[Earth Science]]></category>
		<category><![CDATA[3D forest canopy structure mapping]]></category>
		<category><![CDATA[aboveground biomass]]></category>
		<category><![CDATA[canopy height]]></category>
		<category><![CDATA[ecologists and conservationists GIS tools]]></category>
		<category><![CDATA[forest carbon]]></category>
		<category><![CDATA[forest disturbance response analysis]]></category>
		<category><![CDATA[forest structure]]></category>
		<category><![CDATA[GEDI]]></category>
		<category><![CDATA[geospatial data]]></category>
		<category><![CDATA[global forest monitoring from space]]></category>
		<category><![CDATA[high-resolution vegetation data]]></category>
		<category><![CDATA[integration of spaceborne lidar data into GIS]]></category>
		<category><![CDATA[laser pulse data processing for ecology]]></category>
		<category><![CDATA[NASA EarthData]]></category>
		<category><![CDATA[NASA GEDI forest laser data]]></category>
		<category><![CDATA[open-source GIS tools for ecological research]]></category>
		<category><![CDATA[open-source software]]></category>
		<category><![CDATA[QGIS]]></category>
		<category><![CDATA[QGIS forest analysis plugin]]></category>
		<category><![CDATA[remote sensing]]></category>
		<category><![CDATA[remote sensing forest biodiversity assessment]]></category>
		<category><![CDATA[satellite-based forest carbon measurement]]></category>
		<category><![CDATA[spaceborne LiDAR]]></category>
		<category><![CDATA[tropical forest]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=246826</guid>

					<description><![CDATA[An open-source QGIS plugin called GEDIMetrics now automates the discovery, filtering, and fusion of NASA's GEDI spaceborne LiDAR products, making forest height, biomass, and structural complexity data accessible to non-programmers.]]></description>
										<content:encoded><![CDATA[<p>Forests store an enormous share of the planet&#8217;s carbon, and the three-dimensional architecture of their canopies determines how much of that carbon they can hold, how much habitat they provide, and how they respond to disturbance. For decades, measuring that vertical structure meant costly field campaigns or airborne laser surveys that covered only small, discontinuous patches of land. NASA&#8217;s Global Ecosystem Dynamics Investigation, known as GEDI, changed the equation by firing billions of laser pulses at forests from the International Space Station, producing near-global, high-resolution three-dimensional snapshots of vegetation between 51.6 degrees north and south of the equator. Now, a team of researchers has removed one of the last practical barriers between that torrent of spaceborne data and the ecologists, foresters, and conservationists who need it.</p>
<p>In a study published in Earth Science Informatics, Alexander Cotrina-Sanchez and Michele Torresani of the Free University of Bozen-Bolzano, together with Leonel Corado of the Universidade de Évora, present GEDIMetrics, an open-source plugin for the widely used geographic information system QGIS. The tool integrates the entire GEDI processing chain, from discovering and downloading raw data files to filtering, clipping, and fusing four complementary data products into a single analysis-ready dataset, all through a graphical interface that requires no programming. The plugin is freely available through the official QGIS Plugin Repository and on GitHub under the GNU General Public License.</p>
<p>The technical challenge the plugin addresses is deceptively simple to describe but notoriously tedious in practice. GEDI&#8217;s laser footprints, roughly 25 meters in diameter and spaced about 60 meters apart along the satellite&#8217;s track, capture the vertical distribution of returned laser energy. From these waveforms, NASA derives several distinct products: Level 2A provides canopy height and ground elevation metrics, Level 2B characterizes vertical canopy structure including canopy cover, plant area index, and foliage height diversity, Level 4A delivers aboveground biomass density estimates from globally calibrated models, and Level 4C offers the Waveform Structural Complexity Index, a machine-learning-derived measure of three-dimensional canopy complexity. Each product, however, is distributed as independent HDF5 files organized by laser beam, and the products must be aligned using a unique identifier called the shot number before any joint analysis becomes possible.</p>
<p>Existing tools each solved only fragments of this puzzle. NASA&#8217;s EarthData Search portal handles discovery and download but performs no subsetting, filtering, or cross-product integration. Programming libraries such as rGEDI and pyGEDI offer flexible scripted processing but demand coding expertise. Command-line frameworks like GEDI-Pipeline introduced automation, yet none provided a graphical workflow suitable for non-programmers, and none supported automated multi-product merging. GEDIMetrics closes that gap with a five-stage pipeline: granule discovery through NASA&#8217;s Common Metadata Repository API, authenticated download from EarthData, variable extraction with quality filtering, spatial subsetting to a user-defined region, and footprint-level merging of the selected products, followed by export to standard geospatial formats such as GeoPackage and GeoParquet.</p>
<p>The engineering behind the plugin reflects careful attention to both performance and reproducibility. Spatial filtering proceeds in two stages, beginning with a fast bounding-box pre-filter and followed by precise point-in-polygon clipping using Shapely geometric operations, an approach that substantially reduces processing time for granules covering far more area than the target region. Because data availability can differ across products due to variations in temporal coverage, algorithm convergence, or quality criteria, the merging stage uses Level 2A as the base product and offers configurable join strategies: an inner join retains only footprints present in all selected products, guaranteeing cross-product consistency, while an outer join preserves maximum spatial coverage at the cost of null values. Output files embed metadata recording the full processing configuration, including selected products, temporal range, region geometry, quality thresholds, and plugin version, ensuring that every analysis can be reproduced exactly.</p>
<p>Quality filtering, a critical step for GEDI data, is handled through an intuitive interface. Users can set minimum thresholds for product-specific quality flags, exclude footprints degraded by cloud or atmospheric effects, restrict analysis to land surfaces, and apply a global minimum beam sensitivity threshold, defaulting to 0.90 following criteria established for broad-scale applications. The sensitivity threshold can be raised for particular ecosystems, for example to 0.96 for temperate forests or higher for dense tropical canopies where the laser signal struggles to penetrate to the ground. A logging panel reports the number of granules identified and the estimated data volume before download begins, allowing users to adjust their parameters before committing to lengthy retrievals.</p>
<p>To demonstrate the plugin&#8217;s capabilities, the team tested GEDIMetrics across two contrasting forest ecosystems of roughly 100 square kilometers each: a temperate mixed forest in northeastern France and a humid tropical rainforest in the Madre de Dios region of southeastern Peru, an area partially overlapping the Tambopata National Reserve where intact forest faces mounting pressure from illegal gold mining. Using data from March 2019 to April 2023 with default quality settings, the temperate site yielded 96 granules and 5,939 forested footprints, while the tropical site produced only 23 granules and 1,712 footprints, a disparity that reflects the International Space Station&#8217;s orbital geometry, which delivers more frequent coverage at mid-latitudes than near the equator.</p>
<p>The case study also revealed striking asymmetries in product-level data availability that cannot be inferred from footprint counts alone. Retention of the Level 2B canopy structure product was moderate at the temperate site, at 60.8 percent of forested footprints, but nearly absent at the tropical site, at just 0.9 percent. The biomass product showed the inverse pattern, with 7.2 percent retention in France versus 87.2 percent in Peru. Despite these differences, the merged datasets painted a coherent ecological picture: the tropical forest exhibited taller canopies, with a 98th-percentile height of 24.05 meters compared to 18.86 meters at the temperate site, higher aboveground biomass density of 157.49 versus 139.51 megagrams per hectare, and greater structural complexity. Most strikingly, footprints inside the Tambopata National Reserve showed consistently taller canopies, 38 percent higher biomass density, and higher structural complexity than those in the surrounding buffer zone, a quantifiable signature of the degradation pressure from gold mining at the reserve&#8217;s edges.</p>
<p>At the temperate site, the plugin&#8217;s integrated dataset captured seasonal phenology with unexpected clarity. Canopy cover and plant area index rose sharply during the April-to-October vegetative period, consistent with the flush of deciduous foliage, while canopy height remained essentially stable across seasons, confirming that height metrics are largely insensitive to phenological state. The most dramatic seasonal signal appeared in the median height percentile, which jumped from 1.27 meters in the leafless months to 6.36 meters during the growing season, reflecting the increased interception of laser energy by mid-canopy leaves. This ability to distinguish genuine structural change from seasonal foliage dynamics has direct implications for disturbance monitoring and carbon accounting.</p>
<p>The researchers are candid about current limitations. Processing is single-machine and sequential, which can make large regions slow to analyze, and the plugin does not yet correct GEDI&#8217;s footprint geolocation uncertainty of roughly 10 meters, though its modular design allows integration with external correction tools. Future development priorities include polygon-level summary statistics, diagnostics quantifying footprint loss at each filtering stage, in-plugin visualization of vertical foliage profiles, and a hybrid local-cloud workflow leveraging NASA&#8217;s evolving cloud-native archives. The team also envisions extending the plugin to ICESat-2 canopy height data, which would push coverage beyond GEDI&#8217;s latitudinal limits into boreal and high-latitude forests. For now, GEDIMetrics stands as a quietly transformative piece of software: by collapsing a multi-step, script-heavy workflow into a transparent graphical process inside the world&#8217;s most widely used open-source GIS, it puts the vertical architecture of the world&#8217;s forests within reach of anyone with a computer, a QGIS installation, and a free NASA EarthData account.</p>
<p><strong>Subject of Research:</strong> An open-source QGIS plugin for accessing, filtering, and fusing NASA GEDI spaceborne LiDAR forest structure data products</p>
<p><strong>Article Title:</strong> GEDIMetrics: a QGIS plugin for accessing and integrating multi-product GEDI spaceborne LiDAR data</p>
<p><strong>Article References:</strong> Cotrina-Sanchez, A., Torresani, M., &amp; Corado, L. (2026). GEDIMetrics: a QGIS plugin for accessing and integrating multi-product GEDI spaceborne LiDAR data. <em>Earth Science Informatics, 19</em>(11), Article 205. <a href="https://doi.org/10.1007/s12145-026-02254-z" rel="noopener noreferrer">https://doi.org/10.1007/s12145-026-02254-z</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.1007/s12145-026-02254-z" rel="noopener noreferrer">10.1007/s12145-026-02254-z</a></p>
<p><strong>Keywords:</strong> GEDI, spaceborne LiDAR, QGIS, forest structure, aboveground biomass, canopy height, remote sensing, open-source software, geospatial data, NASA EarthData, tropical forest, forest carbon</p>
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		<post-id xmlns="com-wordpress:feed-additions:1">246826</post-id>	</item>
		<item>
		<title>Genomes Show Fiji&#8217;s Tiny Canopy Bees Have Lost 99% of Their Population</title>
		<link>https://scienmag.com/genomes-show-fijis-tiny-canopy-bees-have-lost-99-of-their-population/</link>
		
		<dc:creator><![CDATA[Gavin Prescott]]></dc:creator>
		<pubDate>Thu, 08 Oct 2026 00:05:02 +0000</pubDate>
				<category><![CDATA[Biology]]></category>
		<category><![CDATA[African tulip tree]]></category>
		<category><![CDATA[biodiversity loss in Fiji's mountain forests]]></category>
		<category><![CDATA[canopy ecology]]></category>
		<category><![CDATA[conservation]]></category>
		<category><![CDATA[cryptic pollinator loss in tropical forests]]></category>
		<category><![CDATA[effective population size]]></category>
		<category><![CDATA[effects of cyclones on island insect populations]]></category>
		<category><![CDATA[effects of deforestation on island pollinators]]></category>
		<category><![CDATA[Fiji]]></category>
		<category><![CDATA[Fiji canopy bees population decline]]></category>
		<category><![CDATA[forest canopy specialist bee species]]></category>
		<category><![CDATA[genome analysis of endangered bees]]></category>
		<category><![CDATA[Hylaeus bees]]></category>
		<category><![CDATA[impact of colonization on native species]]></category>
		<category><![CDATA[Invasive Species]]></category>
		<category><![CDATA[invasive trees and native bee habitat]]></category>
		<category><![CDATA[IUCN Red List]]></category>
		<category><![CDATA[long-term decline of tiny tropical pollinators]]></category>
		<category><![CDATA[Pollinator decline]]></category>
		<category><![CDATA[population genomics]]></category>
		<category><![CDATA[population genomics of endemic Fiji bees]]></category>
		<category><![CDATA[species distribution modelling]]></category>
		<category><![CDATA[tropical bee conservation challenges]]></category>
		<category><![CDATA[tropical forest]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=245846</guid>

					<description><![CDATA[Genomic analysis of Fiji's tiny canopy-dwelling Hylaeus bees reveals a 99 percent population collapse over 150 years, driven by colonisation, deforestation, cyclones and an invasive toxic tree.]]></description>
										<content:encoded><![CDATA[<p>Deep in the mountain forests of Viti Levu, Fiji&#8217;s largest island, lives a group of bees so small, so elusive, and so tied to the forest canopy that scientists only described them formally in 2024. Now, a new genomic study has delivered a sobering verdict on their fate: the most abundant of these bees, a species named Hylaeus navai, has lost roughly 99 percent of its effective population size over the past 150 years, a collapse that closely tracks European colonisation, deforestation, cyclones and the spread of a toxic invasive tree. The findings, published in Ecology and Evolution, offer one of the clearest genetic portraits yet of a cryptic pollinator decline in the tropics, and they suggest that many similar collapses may be going undetected in forest canopies around the world.</p>
<p>The research team, led by scientists at the University of Wollongong in Australia, combined systematic field surveys, population genomics and species distribution modelling to assess the conservation status of Fiji&#8217;s endemic Hylaeus bees. These tiny insects, averaging just 3.9 millimetres in body length, belong to a radiation of six canopy-specialist species found nowhere else on Earth. Unlike most bees, they carry pollen internally in their crops rather than on external hairs, and they appear to specialise on red-flowered canopy plants, a preference that challenges the long-standing assumption that bees cannot see red. Their small size likely limits their foraging ranges, making them particularly vulnerable to habitat fragmentation and forest disturbance.</p>
<p>Sampling these bees posed a formidable challenge. The team designed a stratified, randomised survey across Viti Levu, dividing the island into elevational bands and land-use categories, and generating 36 primary sampling sites along the road network, with 36 auxiliary sites as backups. At each site, crews of three to five people worked in parallel: one person always sweep-netting low vegetation with a standard net, and at least one person always deploying a specialised canopy net extending nine to fourteen metres into the treetops. This dual approach was essential, because traditional ground-level surveys systematically miss entire pollinator communities living in the canopy. Between April 14 and May 11, 2025, the team visited 54 locations and collected 101 Hylaeus specimens, dominated by the species Geissois superba and Metrosideros collina as floral hosts.</p>
<p>The elevational patterns were immediately striking. Hylaeus navai and H. veli were found only between 875 and 1,334 metres, while H. derectus ranged from 371 to 900 metres and H. albaeus from 3 to 923 metres. Critically, of the 26 randomly generated sites below 600 metres, the team collected only a single Hylaeus specimen, despite nearly an hour of average sampling effort per site. This near-total absence from lowlands, where historical records from 1970 to 2016 show these bees were once present, is deeply concerning and points to possible extirpations across Fiji&#8217;s lowland forests, which make up 78 percent of the country&#8217;s forested area.</p>
<p>To read the demographic history written into the bees&#8217; genomes, the researchers sequenced genome-wide single nucleotide polymorphisms from 94 specimens using Diversity Arrays Technology, filtering the raw data down to 4,839 high-quality loci for the focal species H. navai. They supplemented this with mitochondrial COI barcoding from 16 pinned representatives, sequenced rapidly using Oxford Nanopore technology at the Australian National University. The nuclear data revealed a single, panmictic population of H. navai across the highland forests: principal component analyses, discriminant analyses and ancestry coefficient estimates all pointed to one interbreeding population, with no significant isolation by distance. This genetic uniformity likely reflects ongoing gene flow through the contiguous highland forest, though the COI phylogeny revealed clear divergence between island populations on Viti Levu and Taveuni, hinting that structure emerges at larger geographic scales.</p>
<p>The most dramatic results came from coalescent-based demographic reconstruction using Stairway Plot 2, which infers past effective population size from the site frequency spectrum. Calibrated with a honey bee mutation rate and an estimated six generations per year, based on the life history of the related Hawaiian species Hylaeus anthracinus, the reconstruction revealed a staggering trajectory. A modest decline of about 7 percent began around 1550, plausibly linked to the spread of slash-and-burn agriculture, first evidenced in Fiji around 2,000 years ago. Then, from roughly 1874, coinciding with European colonisation, the declines accelerated sharply. Three separate ten-year windows each saw losses that would individually justify IUCN Red List categories: a 61 percent drop between 1933 and 1942, a 76 percent drop between 2002 and 2011, and an 82 percent drop between 2016 and 2025. Taken together, the effective population size fell by approximately 99 percent over 150 years, with even the most conservative confidence intervals indicating a decline of at least 81.6 percent.</p>
<p>The timing of these crashes aligns with known ecological upheavals. Fiji&#8217;s closed natural forests declined by 21 percent between 1991 and 2007, largely through urban and agricultural expansion. The invasive African tulip tree, introduced as an ornamental in the 1930s, produces nectar toxic to honey bees and stingless bees, and as a red-flowering canopy tree it may act as an ecological trap for the red-flower-specialist Hylaeus. Species distribution models built with MaxEnt showed strong predictive performance, with suitable habitat for H. navai confined to just 1.4 to 2.4 percent of Fiji&#8217;s terrestrial area, concentrated at mid-to-high elevations, while the African tulip tree&#8217;s suitable habitat, covering 13.4 percent of the study area, was largely inverse to the bee&#8217;s, concentrated in the lowlands the bees appear to have abandoned.</p>
<p>Cyclones add another layer of threat. The 2020 population crash coincides with Tropical Cyclone Harold, a category four storm that struck in April of that year. The team also noted that a 2015 specimen of H. albaeus from Rakiraki could not be recollected after Tropical Cyclone Winston devastated the area in 2016, despite repeated targeted efforts in subsequent years. Cyclones destroy canopy cover, fell nest-bearing stems and create disturbed habitat that favours African tulip tree establishment, and projected increases in cyclone intensity under climate change could accelerate these declines further. Warming temperatures, rising by 0.018 to 0.024 degrees Celsius per year in daily maxima across Fiji, may also be narrowing the bees&#8217; suitable elevational niche, as experimental work on related megachilid bees has shown reduced emergence rates at warmer, lower elevations.</p>
<p>Contemporary effective population size estimates from linkage disequilibrium methods were inconsistent across allele frequency thresholds, ranging from 121 to 418, and the researchers chose the most conservative estimate of 121 as the most reliable. Either way, the numbers are extraordinarily small for a species that appears to be the most commonly encountered Hylaeus in Fiji. The authors argue that these findings should form the basis of a Critically Endangered listing for H. navai under IUCN criterion A2b, and they emphasise that the declines show no sign of abating. As populations shrink, proportional losses can accelerate, creating a demographic ratchet that becomes progressively harder to reverse.</p>
<p>Beyond the immediate conservation implications for Fiji, the study offers a transferable framework for detecting cryptic declines in understudied ecosystems worldwide. Canopy-specialist Hylaeus bees are expected to be widespread across the Pacific, linking Australian and French Polynesian taxa, and the threats documented here are likely to affect relatives throughout the region. Only 2.6 percent of the world&#8217;s 21,000 described bee species have been assessed with sufficient data for the IUCN Red List, and research remains heavily skewed toward North America and Western Europe. The authors argue that systematic, multi-strata sampling paired with molecular techniques provides a roadmap for uncovering hidden biodiversity losses, particularly for forest pollinators that traditional ecological surveys never encounter. Without such integrative approaches, entire radiations of specialist pollinators could collapse before anyone knows they exist.</p>
<p><strong>Subject of Research:</strong> Population genomics and conservation status of endemic canopy-specialist Hylaeus bees in Fiji</p>
<p><strong>Article Title:</strong> Genomics Reveal Population Crash and Range Contraction in Elusive Fijian Hylaeus Bees</p>
<p><strong>Article References:</strong> Edwards, T. A., Esquerré, D., Johnston, N. P., Galvin, S., Maxwell, N. L., Encinas‐Viso, F., &amp; Dorey, J. B. (2026). Genomics Reveal Population Crash and Range Contraction in Elusive Fijian Hylaeus Bees. <em>Ecology and Evolution, 16</em>(10), Article e74366. <a href="https://doi.org/10.1002/ece3.74366" rel="noopener noreferrer">https://doi.org/10.1002/ece3.74366</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.1002/ece3.74366" rel="noopener noreferrer">10.1002/ece3.74366</a></p>
<p><strong>Keywords:</strong> Hylaeus bees, Fiji, population genomics, pollinator decline, canopy ecology, effective population size, species distribution modelling, invasive species, African tulip tree, IUCN Red List, tropical forest, conservation</p>
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		<post-id xmlns="com-wordpress:feed-additions:1">245846</post-id>	</item>
		<item>
		<title>Forest Edges Lose Trees and Carbon While Interiors Stay Rich, Assam Study Finds</title>
		<link>https://scienmag.com/forest-edges-lose-trees-and-carbon-while-interiors-stay-rich-assam-study-finds/</link>
		
		<dc:creator><![CDATA[Margaret Porter]]></dc:creator>
		<pubDate>Sat, 03 Oct 2026 18:04:08 +0000</pubDate>
				<category><![CDATA[Earth Science]]></category>
		<category><![CDATA[allometric equations]]></category>
		<category><![CDATA[Assam]]></category>
		<category><![CDATA[biodiversity]]></category>
		<category><![CDATA[biodiversity loss at forest edges]]></category>
		<category><![CDATA[biomass measurement in edge versus interior habitats]]></category>
		<category><![CDATA[carbon sequestration]]></category>
		<category><![CDATA[carbon stock]]></category>
		<category><![CDATA[carbon storage decline at forest boundaries]]></category>
		<category><![CDATA[climate change implications for forest carbon sequestration]]></category>
		<category><![CDATA[detailed ecological sampling in Assam forests]]></category>
		<category><![CDATA[disturbance]]></category>
		<category><![CDATA[ecological impacts of urban expansion on forest ecosystems]]></category>
		<category><![CDATA[edge effects]]></category>
		<category><![CDATA[effects of urbanization on forest species richness]]></category>
		<category><![CDATA[Fatasil Reserve Forest]]></category>
		<category><![CDATA[forest ecology]]></category>
		<category><![CDATA[forest edge biodiversity]]></category>
		<category><![CDATA[habitat fragmentation]]></category>
		<category><![CDATA[interior forest resilience to human pressure]]></category>
		<category><![CDATA[stratified random quadrat method in forest studies]]></category>
		<category><![CDATA[tree biomass]]></category>
		<category><![CDATA[tropical forest]]></category>
		<category><![CDATA[tropical forest conservation challenges in India]]></category>
		<category><![CDATA[urban encroachment impact on tropical forests]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=231238</guid>

					<description><![CDATA[A new study of Fatasil Reserve Forest in Assam, India, reveals that the forest's interior holds nearly twice the tree species richness, biomass, and carbon stock of its heavily disturbed urban edge.]]></description>
										<content:encoded><![CDATA[<p>A small reserve forest on the edge of one of India&#8217;s fastest-growing cities has become an unlikely laboratory for one of ecology&#8217;s most consequential questions: what happens to a forest&#8217;s biodiversity and its capacity to store carbon as human pressure pushes inward from the boundary? A new study of Fatasil Reserve Forest in Assam, published in the journal Environmental Monitoring and Assessment, has quantified that transition with unusual precision, and the numbers tell a story that will resonate far beyond this single patch of tropical woodland. Researchers from the Department of Botany at Cotton University in Guwahati divided the forest into two distinct habitats, an edge habitat exposed to the surrounding urban landscape and an interior habitat shielded deeper within the stand, and then measured everything from species richness to total biomass across the two zones.</p>
<p>The scale of the fieldwork alone sets the study apart. Using a stratified random quadrat method, the team laid out a total of 1,050 quadrats of different sizes across the forest, a sampling intensity that allowed them to capture the fine-grained structure of the tree community rather than relying on a handful of broad transects. Within each quadrat they recorded tree species identity, counted individual stems, measured trunk diameters at breast height, the standard forestry metric abbreviated as DBH, and calculated total basal cover, a measure of the ground area occupied by tree trunks that serves as a proxy for the dominance and developmental stage of a stand. From these raw measurements they derived a battery of classical ecological indices, including the Shannon-Weiner diversity index, Margalef&#8217;s species richness index, Simpson&#8217;s index of dominance, and Pielou&#8217;s species evenness index, each of which captures a different facet of how biological variety is organized in a community.</p>
<p>The contrast between the two habitats was stark. The interior habitat harbored 38 tree species, compared with only 22 in the edge habitat, and its stem density reached 1,460 stems per hectare against 1,093.33 stems per hectare at the edge. Total basal cover followed the same pattern, standing at 84.41 square meters per hectare in the interior versus 50.05 square meters per hectare at the edge, indicating that interior trees were not merely more numerous but also larger and structurally more dominant. The Shannon-Weiner diversity index, which blends species richness with the relative abundance of each species, scored 3.49 in the interior against 2.90 at the edge, while Margalef&#8217;s richness index registered 5.29 versus 3.13. In every measure of diversity and structural complexity, the deep forest outperformed its own margin.</p>
<p>Yet the edge habitat was not simply an impoverished version of the interior. Two indices actually favored the boundary zone: Simpson&#8217;s index, which measures the probability that two randomly drawn individuals belong to the same species, was higher at the edge at 0.07 compared with 0.04 in the interior, and Pielou&#8217;s evenness index reached 1.07 at the edge against 1.04 inside. These values suggest that although fewer species live at the edge, the individuals that do survive there are distributed more evenly among those species, a pattern often observed in disturbed environments where hardy, generalist species proliferate without any single one dominating. When the researchers subjected the tree communities of the two habitats to statistical comparison, the difference in species diversity proved highly significant at the p less than or equal to 0.01 level, confirming that the edge-interior gradient represents a genuine ecological discontinuity rather than random variation.</p>
<p>Disturbance emerged as the most likely driver of the divide. By applying a disturbance index to each habitat, the team found that the edge habitat had suffered 38.69 percent disturbance, nearly four times the 9.25 percent recorded in the interior. Fatasil Reserve Forest sits within the Kamrup Metropolitan District, pressed against the expanding city of Guwahati, and its margins absorb the brunt of human activity, from fuelwood collection and grazing to encroachment and the microclimatic changes that follow when a closed canopy is opened to the sky. Edge effects of this kind are among the most extensively documented phenomena in conservation biology. Fragmented habitats expose interior species to altered light, temperature, wind, and humidity regimes, and the landmark long-term studies of Amazonian forest fragments cited in the paper have shown that such changes can trigger cascading losses of biodiversity that deepen over decades.</p>
<p>The carbon story proved equally dramatic, if statistically subtler. Total biomass in the interior habitat reached 1,023.62 megagrams per hectare, nearly double the 535.86 megagrams per hectare found at the edge. Converting biomass to carbon using standard allometric formulas and the widely applied assumption that roughly half of dry biomass is carbon, the researchers estimated a total carbon stock of 511.81 megagrams of carbon per hectare in the interior versus 267.93 megagrams of carbon per hectare at the edge. Expressed in terms of climate impact, the carbon dioxide equivalent came to 1,878.34 megagrams per hectare in the interior and 983.30 megagrams per hectare at the edge. In other words, the protected heart of this forest holds almost twice the climate-warming carbon of its exposed rim, and the difference between the two zones amounts to hundreds of megagrams of carbon dioxide equivalent per hectare.</p>
<p>Interestingly, when the researchers ran their statistical tests, the differences in total biomass, total carbon stock, and carbon dioxide equivalent between the two habitats did not reach significance at the p less than or equal to 0.01 threshold, even though the raw values differed substantially. The authors attribute the pattern to the enormous contribution of large-diameter trees, whose individual biomass can outweigh that of dozens of smaller stems, introducing high variability into the estimates. What did emerge as highly significant was the distribution of carbon across diameter classes. Carbon stock differed significantly among DBH classes in both habitats, peaking in the 20.1 to 30 centimeter class. This finding carries practical weight: mid-sized trees, large enough to accumulate serious woody biomass but still in their vigorous growth phase, are the workhorses of carbon sequestration in this forest, and any management action that removes or suppresses this size class would disproportionately undermine the forest&#8217;s climate function.</p>
<p>The biomass estimates themselves rest on allometric equations, the mathematical models that translate easily measured variables such as trunk diameter into harder-to-measure quantities like total aboveground mass. The study draws on the pantropical allometric frameworks refined by Chave and colleagues, which were calibrated through destructive sampling of trees across the tropics, alongside root biomass allocation factors developed for upland forests to account for the belowground component. This methodological lineage matters because carbon accounting for forests underpins everything from national greenhouse gas inventories to REDD+ programs that pay developing countries to keep their forests standing. When a study demonstrates that a single reserve forest can vary by nearly 250 megagrams of carbon per hectare between its edge and its interior, it underscores how coarse national averages can mask the fine-scale heterogeneity that determines where conservation dollars actually buy the most carbon.</p>
<p>The context of Fatasil Reserve Forest makes these findings especially urgent. Guwahati is one of the most rapidly urbanizing cities in northeastern India, and its green fragments serve double duty as biodiversity refuges and as buffers against urban heat, air pollution, and flooding. The reserve also features in documented human-wildlife interactions, including leopards moving through the urban matrix, a reminder that these fragments are living ecosystems rather than ornamental parks. Previous work by the same research group has examined tree diversity in Assam&#8217;s tropical moist deciduous forests, biomass in urban campus trees, and carbon stored by roadside plantings in Guwahati, building a picture of how vegetation across the urban-rural gradient of the region stores and cycles carbon. The new edge-interior analysis adds a critical dimension to that picture by showing that the value of a forest fragment is not uniform across its area.</p>
<p>The management implications are clear and the authors state them directly: the interior habitat&#8217;s ecological significance and carbon sequestration potential deserve protection, while the edge habitat requires targeted interventions to arrest its degradation. Buffer plantings, restrictions on biomass extraction, and restoration of degraded margins could shrink the effective edge zone and allow interior conditions to expand, a strategy consistent with global evidence that edge effects diminish as fragments grow or as their boundaries are softened. For a forest holding over 1,800 megagrams of carbon dioxide equivalent per hectare in its interior, the stakes of such interventions extend from the neighborhoods of Guwahati to the global climate ledger. As tropical forests worldwide continue to be carved into ever smaller pieces, studies like this one provide the quantitative grounding needed to argue that what happens at the edge of a forest is never confined to its edge.</p>
<p><strong>Subject of Research:</strong> Edge-interior variation in tree diversity, community structure, and carbon stock in a tropical reserve forest in Assam, India</p>
<p><strong>Article Title:</strong> Disparities in species diversity, community characteristics, and carbon stock of trees along the edge-interior gradient of Fatasil Reserve Forest, Assam, India</p>
<p><strong>Article References:</strong> Kalita, P., &amp; Yumnam, J. Y. (2026). Disparities in species diversity, community characteristics, and carbon stock of trees along the edge-interior gradient of Fatasil Reserve Forest, Assam, India. <em>Environmental Monitoring and Assessment, 198</em>(10), Article 1120. <a href="https://doi.org/10.1007/s10661-026-15966-y" rel="noopener noreferrer">https://doi.org/10.1007/s10661-026-15966-y</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.1007/s10661-026-15966-y" rel="noopener noreferrer">10.1007/s10661-026-15966-y</a></p>
<p><strong>Keywords:</strong> forest ecology, edge effects, carbon stock, biodiversity, tree biomass, Fatasil Reserve Forest, Assam, habitat fragmentation, disturbance, allometric equations, tropical forest, carbon sequestration</p>
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		<post-id xmlns="com-wordpress:feed-additions:1">231238</post-id>	</item>
		<item>
		<title>Camera Traps Reveal Hidden Shifts in Tropical Fruit-Eating Wildlife as Forest Disturbance Rises</title>
		<link>https://scienmag.com/camera-traps-reveal-hidden-shifts-in-tropical-fruit-eating-wildlife-as-forest-disturbance-rises/</link>
		
		<dc:creator><![CDATA[Margaret Porter]]></dc:creator>
		<pubDate>Wed, 30 Sep 2026 18:15:26 +0000</pubDate>
				<category><![CDATA[Biology]]></category>
		<category><![CDATA[camera trap studies in French Guiana]]></category>
		<category><![CDATA[camera traps]]></category>
		<category><![CDATA[canopy ecology]]></category>
		<category><![CDATA[changes in animal community composition due to habitat disturbance]]></category>
		<category><![CDATA[conservation]]></category>
		<category><![CDATA[conservation implications for tropical fruit-eating species]]></category>
		<category><![CDATA[disturbance]]></category>
		<category><![CDATA[ecological shifts in rainforest biodiversity]]></category>
		<category><![CDATA[effects of logging and hunting on forest species]]></category>
		<category><![CDATA[forest disturbance gradients and wildlife responses]]></category>
		<category><![CDATA[French Guiana]]></category>
		<category><![CDATA[frugivores]]></category>
		<category><![CDATA[fruit-eating animals in tropical ecosystems]]></category>
		<category><![CDATA[hunting]]></category>
		<category><![CDATA[impact of human disturbance on frugivorous animals]]></category>
		<category><![CDATA[kinkajou]]></category>
		<category><![CDATA[long-term wildlife monitoring with camera traps]]></category>
		<category><![CDATA[role of seed predators and dispersers in forest dynamics]]></category>
		<category><![CDATA[seed dispersal]]></category>
		<category><![CDATA[seed dispersal and forest regeneration]]></category>
		<category><![CDATA[tropical forest]]></category>
		<category><![CDATA[Tropical rainforest wildlife monitoring]]></category>
		<category><![CDATA[Virola]]></category>
		<category><![CDATA[white-lipped peccary]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=217922</guid>

					<description><![CDATA[A camera trap study in French Guiana shows that fruit-eating vertebrate communities keep their species richness under disturbance but undergo major shifts in visitation rates and dominant species.]]></description>
										<content:encoded><![CDATA[<p>Deep in the rainforests of French Guiana, the fate of entire forest communities may rest on the shoulders, wings and paws of fruit-eating animals. Frugivorous vertebrates—the monkeys, birds, rodents and other creatures that consume fruit—are far more than casual diners. As seed dispersers and seed predators, they shape which trees regenerate, where seedlings take root and how forest composition evolves over decades. A new study published in Ecology and Evolution has now tracked how these vital animal communities respond to different histories of human disturbance, and the results reveal a subtle but consequential reshuffling of tropical wildlife that simple species counts would completely miss.</p>
<p>An international research team deployed 60 camera traps at nutmeg trees of the species Virola kwatae and Virola michelii, members of the Myristicaceae family, across three forest sites in French Guiana subjected to contrasting levels of human pressure. The first site was a protected mature forest, the least disturbed of the three. The second was a formerly exploited forest representing an intermediate disturbance level, where past human use had left its mark but active pressures had eased. The third and most disturbed site bordered a road and faced ongoing hunting and logging activity. By positioning cameras both on the forest floor and high in the canopy at fruiting nutmeg trees, the researchers captured a two-tiered portrait of the frugivore communities that few studies have attempted.</p>
<p>The most striking initial finding was what did not change. Species richness—the raw number of fruit-eating vertebrate species visiting the trees—remained remarkably consistent across all three sites. The canopy hosted 19 to 20 species at each location, while the understory supported 14 to 16. On paper, this might suggest that even the most heavily disturbed forest retains its full complement of seed dispersers. But the deeper analysis told a very different story, one that carries important lessons for how conservationists measure ecosystem health.</p>
<p>While the cast of characters stayed the same, the frequency of their appearances shifted dramatically. Terrestrial frugivore visitation rates fell sharply as disturbance increased, dropping from 232.5 plus or minus 53.7 individuals per 100 trap-days at the protected site to just 87.2 plus or minus 11.2 at the most disturbed site—a decline of more than 60 percent. In stark contrast, arboreal visitation rates moved in the opposite direction, tending to rise with disturbance, from 43.5 plus or minus 12.5 at the protected forest to 80.3 plus or minus 16 at the most disturbed one. The forest floor was emptying out even as the canopy grew busier, a pattern that hints at fundamentally different vulnerabilities between ground-dwelling and tree-dwelling fruit eaters.</p>
<p>The identity of the winners and losers proved equally revealing. In the canopy of the most disturbed site, visits were dominated by kinkajous (Potos flavus) and golden-handed tamarins (Saguinus midas), two arboreal species that appeared to thrive or at least persist under pressure. Meanwhile, in the understory of that same site, visitation rates dropped significantly for what the researchers classify as sensitive species—those with low reproductive rates or those targeted by hunters. Among the casualties were white-lipped peccaries (Tayassu pecari), large-bodied mammals that move seeds across long distances, and gray-winged trumpeters (Psophia crepitans), ground-dwelling birds known for their ecological sensitivity. The loss of such species is not merely a matter of biodiversity bookkeeping; each removal alters the seed dispersal services the forest depends upon.</p>
<p>To understand what drives these community patterns, the team modeled how environmental and site-level variables predicted assemblage composition, and the results differed sharply between the two vertical strata. In the canopy, four factors emerged as significant predictors of which species assembled at a given tree: the identity of the site itself, the diameter of the tree, the availability of fruit and the degree of canopy cover. This suggests that arboreal frugivores respond to a rich combination of landscape history and local resource structure, choosing their feeding grounds based on both the immediate payoff and the surrounding habitat conditions.</p>
<p>The understory told a simpler and arguably more troubling story. None of the measured micro-habitat variables contributed significantly to the structure of terrestrial frugivore assemblages. Instead, site identity was the single significant predictor. In other words, what mattered for ground-dwelling fruit eaters was not the local vegetation structure or fruiting conditions at a particular tree, but the disturbance history of the landscape as a whole. This pattern is consistent with the idea that hunting pressure and broad-scale human access, rather than fine-scale habitat features, are the dominant forces filtering terrestrial frugivore communities in these forests.</p>
<p>The methodological approach deserves attention for what it reveals about tropical ecology. Camera traps aimed at fruiting trees provide a standardized, non-invasive window into animal communities across vertical strata that are notoriously difficult to survey. Canopy wildlife is often invisible to ground-based observers, and many frugivores are cryptic, nocturnal or wary of humans. By monitoring the same nutmeg trees from below and above, the researchers could compare the responses of arboreal and terrestrial assemblages within the same resource patches, isolating the effects of disturbance history from those of food availability. The finding that the two strata responded in opposite directions would have been impossible to detect with ground-level surveys alone.</p>
<p>Why does this matter beyond French Guiana? Frugivorous vertebrates underpin the regeneration of large-seeded, animal-dispersed trees across the tropics, and nutmeg trees are a classic example of a plant that depends on specialized dispersers. When hunting strips the forest floor of peccaries and trumpeters, the seeds of these trees may pile up beneath parent plants, fall prey to seed predators, or fail to reach the light gaps they need to establish. Over time, such changes can shift forest composition toward tree species with abiotic or small-animal dispersal, rewiring ecosystem processes in ways that may take centuries to reverse. The apparent stability of species richness in this study serves as a warning: a forest can look intact on a checklist while its functional machinery quietly degrades.</p>
<p>The study&#8217;s conclusions carry clear implications for conservation planning. The researchers emphasize the importance of considering species-specific responses and the disturbance histories of individual sites, rather than relying on coarse measures of biodiversity. They also highlight the value of protected areas and forests under active restoration in maintaining functional frugivore assemblages. The intermediately disturbed site, once exploited but now recovering, offers a note of cautious optimism: forests given room to heal can retain much of their ecological function. But the most disturbed site, with its depleted ground-level community and kinkajou-dominated canopy, shows what happens when roads, logging and hunting converge. As tropical landscapes face mounting pressure, this research makes the case that protecting not just the number of species but the full functional web of seed dispersers is essential to keeping rainforests alive from the forest floor to the treetops.</p>
<p><strong>Subject of Research:</strong> Responses of arboreal and terrestrial frugivore vertebrate assemblages to human disturbance histories in French Guianan tropical forests</p>
<p><strong>Article Title:</strong> Arboreal and Terrestrial Frugivore Vertebrate Assemblage Diversity and Composition Vary With Disturbance Histories in Guianan Forests</p>
<p><strong>Article References:</strong> Abensur, R., Coutant, O., Gloaguen, P., Gottstein, M., Pelon, C., Guilbert, E., Baltzinger, C., &amp; Forget, P.-M. (2026). Arboreal and Terrestrial Frugivore Vertebrate Assemblage Diversity and Composition Vary With Disturbance Histories in Guianan Forests. <em>Ecology and Evolution, 16</em>(10), Article e74374. <a href="https://doi.org/10.1002/ece3.74374" rel="noopener noreferrer">https://doi.org/10.1002/ece3.74374</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.1002/ece3.74374" rel="noopener noreferrer">10.1002/ece3.74374</a></p>
<p><strong>Keywords:</strong> French Guiana, frugivores, seed dispersal, camera traps, tropical forest, disturbance, hunting, kinkajou, white-lipped peccary, canopy ecology, conservation, Virola</p>
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		<post-id xmlns="com-wordpress:feed-additions:1">217922</post-id>	</item>
		<item>
		<title>Managed Zones Harbor Richer Forests Amid Widespread Degradation in Nigerian Reserve</title>
		<link>https://scienmag.com/managed-zones-harbor-richer-forests-amid-widespread-degradation-in-nigerian-reserve/</link>
		
		<dc:creator><![CDATA[Margaret Porter]]></dc:creator>
		<pubDate>Sat, 12 Sep 2026 01:15:31 +0000</pubDate>
				<category><![CDATA[Earth Science]]></category>
		<category><![CDATA[community-based forest conservation Nigeria]]></category>
		<category><![CDATA[conservation management]]></category>
		<category><![CDATA[deforestation rates in Nigeria]]></category>
		<category><![CDATA[effects of agricultural expansion on Nigerian forests]]></category>
		<category><![CDATA[effects of infrastructure development on Nigerian forests]]></category>
		<category><![CDATA[endangered Nigeria-Cameroon chimpanzee habitat]]></category>
		<category><![CDATA[forest degradation]]></category>
		<category><![CDATA[forest management and protection strategies]]></category>
		<category><![CDATA[forest structure]]></category>
		<category><![CDATA[impacts of illegal logging in Nigeria]]></category>
		<category><![CDATA[Ise Forest Reserve]]></category>
		<category><![CDATA[Ise Forest Reserve biodiversity]]></category>
		<category><![CDATA[land-cover change]]></category>
		<category><![CDATA[Landsat imagery]]></category>
		<category><![CDATA[Nigeria]]></category>
		<category><![CDATA[Nigerian forest conservation]]></category>
		<category><![CDATA[rainforest conservation challenges in Nigeria]]></category>
		<category><![CDATA[remote sensing]]></category>
		<category><![CDATA[restoration ecology]]></category>
		<category><![CDATA[satellite imagery for forest monitoring in Nigeria]]></category>
		<category><![CDATA[secondary forest]]></category>
		<category><![CDATA[tropical forest]]></category>
		<category><![CDATA[tropical forest degradation in Nigeria]]></category>
		<category><![CDATA[vegetation diversity]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=193350</guid>

					<description><![CDATA[A new study finds that the conservation-managed zone of Nigeria's Ise Forest Reserve supports taller, more diverse forest than disturbed areas, even as satellite data reveal widespread land-cover degradation across the reserve between 2016 and 2023.]]></description>
										<content:encoded><![CDATA[<p>Deep in southwestern Nigeria, a fragmented tropical forest reserve is telling a quietly dramatic story about what happens when conservation attention meets relentless human pressure. A new study of the Ise Forest Reserve, published in the journal Discover Forests, has found that the portion of the reserve managed under a dedicated conservation project supports markedly higher tree diversity and stronger forest structure than surrounding disturbed areas, even as satellite records reveal that land-cover degradation swept across the entire landscape between 2016 and 2023. The findings offer both encouragement and a warning: local management can coincide with healthier forest condition, but it has not stopped the wider erosion of one of Nigeria&#8217;s most important rainforest refuges.</p>
<p>Nigeria has lost more than 90 percent of its original forest cover, making it one of the countries with the highest deforestation rates in Africa. Between 2010 and 2015 alone, the country&#8217;s deforestation rate reached roughly five percent, driven by illegal logging, agricultural expansion, and infrastructure development. Ise Forest Reserve, located near the Uso community in Ondo State and spanning parts of Ekiti State, sits squarely within this crisis zone. The reserve is a critical stronghold for the critically endangered Nigeria-Cameroon chimpanzee and also harbors the African forest elephant, the yellow-casqued hornbill, Mona monkeys, and a rich assemblage of plant species including Gmelina arborea, Tectona grandis, and Khaya ivorensis. Despite its protected status, the reserve faces persistent encroachment from loggers and farmers, some of whom clear forestland to cultivate cannabis.</p>
<p>In 2021, the Ekiti State Government took a notable step by gazetting a portion of the reserve to the Southwest/Niger Delta Forest Project for conservation and restoration. The researchers behind the new study seized on this administrative boundary as a natural experiment. They designated the gazetted area as the managed zone and areas outside it as the disturbed zone, then asked a straightforward question: does the managed portion of the forest look ecologically different from the rest? Importantly, the team is careful to note that this division is administrative rather than a measure of true disturbance, and that the managed zone is by no means pristine, having also experienced logging and land-cover change.</p>
<p>To answer the question, the researchers combined painstaking fieldwork with satellite-based remote sensing. In the field, they established eleven sampling plots measuring 25 by 25 meters along transects spaced at least 200 meters apart, with eight plots in the larger managed zone and three in the smaller disturbed zone, allocated proportionally to the mapped area of each zone. Within each plot, they recorded every woody individual, measuring tree height, canopy cover, and diameter at breast height, the standard trunk measurement taken at 1.3 meters above the ground. In total, the survey documented 27 woody species from 17 families. The most frequently recorded species across the reserve was Ricinodendron heudelotii, appearing 55 times, while a single towering Diospyros lotus individual posted the most extreme structural values: a height of 12.20 meters, canopy cover of 18.60 meters, and a trunk diameter of 138.13 centimeters.</p>
<p>The structural comparison between zones was stark. Trees in the managed zone averaged 9.55 meters in height, 4.79 meters of canopy cover, and 21.92 centimeters in trunk diameter, compared with 7.64 meters, 3.35 meters, and 16.77 centimeters respectively in the disturbed zone. Using Welch&#8217;s independent t-tests with a Bonferroni-corrected significance threshold to guard against false positives across the three comparisons, the team found these differences were statistically robust: taller trees (p = 0.002), wider canopies (p &lt; 0.001), and thicker trunks (p &lt; 0.001) all favored the managed zone. Diversity metrics told the same story. The Shannon-Wiener index, which blends species richness with evenness; the Simpson concentration index, which reflects the probability that two randomly drawn individuals belong to the same species; and Margalef&#8217;s richness index all scored higher in the managed zone, which also contained 241 woody individuals across 19 families compared with 75 individuals across 14 families in the disturbed zone.</p>
<p>The satellite analysis painted a far grimmer picture of the wider landscape. Drawing on Landsat 7 and Landsat 9 imagery at 30-meter resolution from November 2016 and December 2023, the researchers classified land cover into secondary forest, degraded vegetation, and farmland, then computed transition rates between the two dates. In the managed zone, secondary forest collapsed from 31.40 square kilometers, or 97.65 percent of the zone, to just 14.10 square kilometers, or 43.85 percent, a net loss of 17.31 square kilometers. Degraded vegetation in the same zone exploded from a mere 0.14 square kilometers to 17.06 square kilometers. In the disturbed zone, farmland surged from 0.54 square kilometers to 7.24 square kilometers, more than a tenfold expansion, while degraded land shifted dramatically in extent. Across the landscape, conversions from secondary forest to degraded vegetation dominated the change matrix, and transitions back toward secondary forest were negligible, hovering around 0.01 percent in both zones.</p>
<p>The spatial contrasts were meaningful as well as the temporal ones. Farmland expanded more slowly in the managed zone than in the disturbed zone, and the loss of secondary forest proceeded at a lower rate there, suggesting that the conservation presence did dampen the most destructive forms of conversion. The species composition also shifted with disturbance. Ricinodendron heudelotii proved resilient and appeared in both zones, while economically valuable timber species such as Milicia excelsa were underrepresented in disturbed areas, consistent with overexploitation of high-value trees. These patterns echo findings from other Nigerian reserves, including Omo Biosphere Reserve, Ago-Owu, and Doma, where logging, fragmentation, and farming have been shown to strip out species diversity, stem density, and structural integrity.</p>
<p>Yet the authors are refreshingly candid about the limits of what their study can claim. Because no vegetation inventory was conducted before the conservation project began in 2021, the study could not use a before-after-control-impact design. The observed differences between zones represent a spatial snapshot, and pre-existing environmental, historical, or accessibility differences between the zones could partly explain them. The researchers explicitly state that the results cannot be attributed solely to the 2021 project and remain subject to review in a long-term evaluation. The two-date satellite comparison, meanwhile, captures net change over seven years but cannot resolve annual fluctuations, seasonal dynamics, fires, or short disturbance pulses that may have occurred in between. Unequal plot replication, dictated by the zones&#8217; different sizes, also means the species counts should be read as field summaries rather than precise estimates of true richness.</p>
<p>Those caveats do not diminish the study&#8217;s central significance. It provides one of the first quantitative baselines for Ise Forest Reserve, coupling ground-truthed structural measurements with remote sensing in a data-scarce landscape, and it demonstrates a replicable template for monitoring restoration efforts across West Africa&#8217;s embattled forest reserves. The picture that emerges is of a landscape under siege but not yet lost: management appears to coincide with taller, thicker, more diverse forest and slower farmland encroachment, even as degraded land expands relentlessly across both zones. The researchers call for intensified patrolling, effective buffer-zone management, community livelihood programs, and rehabilitation of degraded patches. Most critically, they recommend permanent monitoring plots and annual dry-season Landsat or Sentinel-2 imagery to track whether the conservation trajectory truly diverges from the region&#8217;s grim baseline. For the chimpanzees, elephants, and hornbills that depend on Ise, the answer to that question may determine whether the reserve&#8217;s remaining forest endures.</p>
<p>The study&#8217;s methodological choices reflect broader trends in tropical forest monitoring. By pairing ground-based plot inventories with freely available Landsat imagery, the researchers worked within the constraints common to conservation science in data-scarce regions, where funding for extensive field campaigns is limited and historical vegetation records are often absent. Satellite indices such as the Normalized Difference Vegetation Index and the Enhanced Vegetation Index, which track photosynthetic activity from orbit, have become standard tools for detecting vegetation condition across large or inaccessible landscapes, and recent Nigerian studies have shown that machine learning classifiers applied to satellite data can produce usable land-cover maps even where ground information is sparse.</p>
<p>The ecological indicators used in the study each capture a different dimension of forest condition. Species richness counts how many distinct woody species occur in a sample, while the Shannon-Wiener index weighs both richness and the evenness with which individuals are distributed among species, and the Simpson concentration index estimates the probability that two individuals drawn at random belong to the same species. Structural measures such as diameter at breast height, height, and canopy cover complement these diversity metrics because they relate directly to carbon storage, habitat complexity, and the capacity of a forest to support wildlife such as primates that depend on layered canopy and mature fruiting trees.</p>
<p>The reserve&#8217;s setting also matters for interpreting the results. At roughly 366 meters above sea level, with mean annual rainfall of about 1,380 millimeters concentrated in an eight-month wet season from April to October and temperatures ranging between 19 and 30 degrees Celsius, the forest lies within the humid zone of southwestern Nigeria. Its fragmentation, noted by the authors, is itself ecologically significant, since smaller and more isolated forest patches generally support fewer species than large contiguous tracts. A stream near the eastern boundary and the Ogbese River to the west shape the local landscape, while proximity to the Akure-Benin expressway facilitates both access and encroachment.</p>
<p>Finally, the study underscores a persistent challenge for protected-area governance in Nigeria: legal designation alone has not prevented logging, farming, or hunting within reserve boundaries. The authors&#8217; recommendation for permanent monitoring plots and regular dry-season satellite imagery reflects a growing consensus that restoration success must be measured against quantitative baselines rather than assumed from management status, particularly when interventions begin after degradation is already well advanced.</p>
<p><strong>Subject of Research:</strong> Vegetation diversity, forest structure, and land-cover degradation in a managed versus disturbed Nigerian forest reserve</p>
<p><strong>Article Title:</strong> Higher vegetation diversity and stronger forest structure occur in managed zones despite widespread land cover degradation in Ise Forest Reserve Nigeria</p>
<p><strong>Article References:</strong> Olaniyi, O., Ogunsakin, E., Ogunjemite, B., Rafiu, K., &amp; Anozie, E. (2026). Higher vegetation diversity and stronger forest structure occur in managed zones despite widespread land cover degradation in Ise Forest Reserve Nigeria. <em>Discover Forests, 2</em>(1), Article 67. <a href="https://doi.org/10.1007/s44415-026-00129-1" rel="noopener noreferrer">https://doi.org/10.1007/s44415-026-00129-1</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.1007/s44415-026-00129-1" rel="noopener noreferrer">10.1007/s44415-026-00129-1</a></p>
<p><strong>Keywords:</strong> forest degradation, vegetation diversity, Ise Forest Reserve, land-cover change, forest structure, remote sensing, conservation management, Nigeria, tropical forest, Landsat imagery, secondary forest, restoration ecology</p>
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