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	<title>Quercus robur &#8211; Science</title>
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	<title>Quercus robur &#8211; Science</title>
	<link>https://scienmag.com</link>
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		<title>Botanists Seek a New Type for a Misunderstood Iberian Hazelnut Forest</title>
		<link>https://scienmag.com/botanists-seek-a-new-type-for-a-misunderstood-iberian-hazelnut-forest/</link>
		
		<dc:creator><![CDATA[Gavin Prescott]]></dc:creator>
		<pubDate>Mon, 19 Oct 2026 22:11:15 +0000</pubDate>
				<category><![CDATA[Science News]]></category>
		<category><![CDATA[botanical taxonomy challenges]]></category>
		<category><![CDATA[Cantabrian Range]]></category>
		<category><![CDATA[Cantabrian Range plant associations]]></category>
		<category><![CDATA[conserved type]]></category>
		<category><![CDATA[European hazel forest ecosystems]]></category>
		<category><![CDATA[forest ecology and conservation]]></category>
		<category><![CDATA[forest habitat misidentification]]></category>
		<category><![CDATA[forest succession]]></category>
		<category><![CDATA[Galicia]]></category>
		<category><![CDATA[hazel forests]]></category>
		<category><![CDATA[Iberian hazelnut forest classification]]></category>
		<category><![CDATA[Iberian Peninsula]]></category>
		<category><![CDATA[International Code of Phytosociological Nomenclature]]></category>
		<category><![CDATA[oak and hazel forest ecosystems]]></category>
		<category><![CDATA[Omphalodo-Coryletum]]></category>
		<category><![CDATA[Orocantabrian vegetation]]></category>
		<category><![CDATA[phytosociological vegetation types]]></category>
		<category><![CDATA[phytosociology]]></category>
		<category><![CDATA[plant community naming conventions]]></category>
		<category><![CDATA[plant community nomenclature]]></category>
		<category><![CDATA[Quercus robur]]></category>
		<category><![CDATA[secondary forest dynamics]]></category>
		<category><![CDATA[vegetation survey and typification]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=315661</guid>

					<description><![CDATA[A 2022 nomenclature proposal would retain the established Omphalodo-Coryletum name while replacing its atypical oak-forest type with a representative hazel-dominated plot from Galicia.]]></description>
										<content:encoded><![CDATA[<p>A forest association in northwestern Spain has acquired a botanical identity that does not match its official name. The association Omphalodo nitidae-Coryletum avellanae was formally described in 1994 from nut-rich deciduous woods in the westernmost part of the Cantabrian Range, but its designated type specimen came from a different-looking ecosystem: a mature, mesophytic oak forest dominated by Quercus robur. Most of the plots supporting the association instead resembled low, secondary forests in which Corylus avellana, the common or European hazel, formed the principal canopy. A 2022 proposal in Vegetation Classification and Survey asks vegetation scientists to conserve the association’s established name while replacing its type with a representative plot of the hazel forest that later researchers have generally treated as the association’s true subject.</p>
<p>The case illustrates a specialized problem in plant community nomenclature. Unlike the naming of individual species, phytosociological nomenclature attaches names to recurring vegetation assemblages and relies on a type plot to anchor each name in a particular community. A type is intended to resolve ambiguity by showing which vegetation a name refers to. When subsequent fieldwork reveals that most records assigned to a name differ consistently from its original type, however, strict application of the rules can create a mismatch between the label used in scientific literature and the vegetation it formally represents. The authors of the proposal argue that this is precisely what happened with Omphalodo-Coryletum, whose original type was atypical of the association that the name came to designate.</p>
<p>The association was defined using 17 relevés from eastern Lugo province in Galicia, together with a synthetic column assembled from five records in the Terra de Lemos area of the Cabe River basin. These vegetation records documented forests approximately 8 to 10 metres high and generally dominated by hazel, often with a mixture of larger deciduous trees in an upper stratum. The communities also supported numerous shade-associated herbs, including hemicryptophytes and nemoral geophytes. Logging over roughly a century had left much of the sampled vegetation in an immature state, and the original authors interpreted these woods as seral communities that could develop through succession into a more diverse mixed oak forest or even a forest dominated by Quercus pyrenaica.</p>
<p>Most of the 17 records fit that concept of a hazel-dominated secondary forest. Hazel had combined Braun-Blanquet cover values of 4 or 5, meaning that it occupied either a large part of the ground or a clearly dominant share of the vegetation. Other species, including Acer pseudoplatanus, Fraxinus excelsior, Ilex aquifolium and Q. robur, could rise above the hazel canopy, but their cover did not exceed that of the hazel. The selected type relevé was different. It came from Cancelo in Triacastela, Lugo, at 820 metres above sea level, and was dominated by Q. robur with a cover value of 4. Hazel also had a cover value of 4 below the oak canopy, accompanied by Crataegus monogyna, Ilex aquifolium and a rich layer of nemoral herbs. The plot therefore represented a taller, structurally mesophytic oak forest rather than the characteristic physiognomy of the majority of the original records.</p>
<p>Later botanical work sharpened the distinction between the type and the broader body of observations. Studies of Atlantic Iberian forests increasingly separated pre-forest vegetation from mature climatic forests, recognizing that hazel woods can be autonomous pre-climactic communities rather than merely juvenile stages of larger forest types. In influential syntheses of Iberian vegetation, Omphalodo-Coryletum was assigned to the alliance Betulion fontqueri-celtibericae, a group established for pre-forest or “softwood” communities within the class Querco-Fagetea sylvaticae. The name consequently came to represent a seral hazel forest in the western Orocantabrian territory, while the original oak-dominated type was largely treated as an exceptional record. The same interpretation appeared in subsequent floristic inventories and in vegetation checklists for Spain and Portugal.</p>
<p>The proposed solution is based on Article 53 of the fourth edition of the International Code of Phytosociological Nomenclature. As described by the authors, the article permits a name to be maintained with a conserved type when its long-established interpretation has diverged from the original type. The authors are not proposing to abandon Omphalodo nitidae-Coryletum avellanae or rename the community. Instead, they seek a nomenclatural correction that would keep the widely used name and give it a type more consistent with prevailing scientific practice. Such proposals are significant because they can prevent an association name from becoming effectively tied to an atypical habitat while preserving continuity with the literature that has accumulated under that name.</p>
<p>The replacement type is relevé 4 in table 2 of the 1994 publication, rather than the original relevé 12. It was recorded between Moreda and Devesa da Rogueira in Folgoso do Courel, in the Courelian district of the western Orocantabrian sector, at 720 metres above sea level. The site has a 40-degree west-facing slope, 100 percent tree cover, a sampled area of 250 square metres and a total of 41 recorded taxa. Its tree layer includes Corylus avellana with a cover value of 5, together with Acer pseudoplatanus, Castanea sativa, Crataegus monogyna and Ilex aquifolium. The lower layers contain ferns, grasses, woodland herbs and characteristic nemoral plants, creating a structural profile closely aligned with the seral hazel forest recognized in subsequent research.</p>
<p>Several members of the proposed type show why the plot is ecologically informative rather than merely typical. Polystichum setiferum has a cover value of 4, while Hedera hibernica, treated in the record as a subspecies of H. helix, reaches 3. Omphalodes nitida, the species commemorated in the association’s name, is present, along with plants such as Helleborus foetidus, Sanicula europaea, Primula acaulis, Poa nemoralis, Stellaria holostea, Mercurialis perennis and Allium ursinum. The combination of a dense hazel canopy, scattered taller trees and a diverse shaded herb layer captures both the physiognomy and the ecological interpretation of Omphalodo-Coryletum that emerged after 1994. It therefore provides an anchor consistent with the name’s dominant and long-standing use.</p>
<p>Conservation of the new type would also preserve geographic coherence. The original association was defined in the western Orocantabrian subprovince, and nearly all of its original relevés fall in that biogeographical territory. Changes made to regional delimitations after the association was described did not significantly move the relevant western boundary, and the proposed type lies in the same western Orocantabrian sector as the earlier records. The authors therefore argue that the correction does not radically expand the association’s geographic scope or detach the name from its original area of description. Instead, it clarifies the internal relationship between a name, its type and the community consistently recognized under that name. The proposal is ultimately about making plant community taxonomy reflect observed vegetation accurately while allowing the accumulated botanical record to remain usable and internally coherent.</p>
<p><strong>Subject of Research:</strong> Conservation of the phytosociological type for the Omphalodo nitidae-Coryletum avellanae forest association in northwestern Spain.</p>
<p><strong>Article Title:</strong> ﻿Proposal (29) to conserve the name Omphalodo nitidae-Coryletum avellanae Amigo, G. Azcárate et Romero 1994 with a conserved type</p>
<p><strong>Article References:</strong> Rodríguez-Guitián, M. A., &amp; Amigo Vazquez, J. (2022). ﻿Proposal (29) to conserve the name Omphalodo nitidae-Coryletum avellanae Amigo, G. Azcárate et Romero 1994 with a conserved type. <em>Vegetation Classification and Survey, 3</em>, 145-148. <a href="https://doi.org/10.3897/vcs.76387" rel="noopener noreferrer">https://doi.org/10.3897/vcs.76387</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.3897/VCS.76387" rel="noopener noreferrer">10.3897/VCS.76387</a></p>
<p><strong>Keywords:</strong> plant community nomenclature, phytosociology, conserved type, Omphalodo-Coryletum, hazel forests, Quercus robur, Cantabrian Range, Galicia, Orocantabrian vegetation, Iberian Peninsula, forest succession, International Code of Phytosociological Nomenclature</p>
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		<post-id xmlns="com-wordpress:feed-additions:1">315661</post-id>	</item>
		<item>
		<title>Proposal Seeks Typification Fix for an Iberian Oak-Ash Forest</title>
		<link>https://scienmag.com/proposal-seeks-typification-fix-for-an-iberian-oak-ash-forest/</link>
		
		<dc:creator><![CDATA[Margaret Porter]]></dc:creator>
		<pubDate>Mon, 19 Oct 2026 20:58:37 +0000</pubDate>
				<category><![CDATA[Science News]]></category>
		<category><![CDATA[botanical name correction]]></category>
		<category><![CDATA[Cantabrian forests]]></category>
		<category><![CDATA[conserve]]></category>
		<category><![CDATA[conserved neotype]]></category>
		<category><![CDATA[ecological research clarification]]></category>
		<category><![CDATA[European deciduous woodland]]></category>
		<category><![CDATA[forest community typification]]></category>
		<category><![CDATA[Iberian oak-ash forest]]></category>
		<category><![CDATA[Iberian vegetation]]></category>
		<category><![CDATA[International Code of Phytosociological Nomenclature]]></category>
		<category><![CDATA[meso-eutrophic thermophilic forests]]></category>
		<category><![CDATA[name]]></category>
		<category><![CDATA[neotype designation in plant communities]]></category>
		<category><![CDATA[oak-ash forest]]></category>
		<category><![CDATA[phytosociological nomenclature]]></category>
		<category><![CDATA[phytosociology]]></category>
		<category><![CDATA[plant nomenclature]]></category>
		<category><![CDATA[Polysticho]]></category>
		<category><![CDATA[Polysticho setiferi-Fraxinetum excelsioris]]></category>
		<category><![CDATA[proposal]]></category>
		<category><![CDATA[Quercus robur]]></category>
		<category><![CDATA[Quercus robur and Fraxinus excelsior habitat]]></category>
		<category><![CDATA[vegetation classification in northern Spain and France]]></category>
		<category><![CDATA[vegetation map standardization]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=315243</guid>

					<description><![CDATA[A nomenclatural proposal would preserve a widely used Iberian forest name while replacing a beech-dominated type with a conserved neotype that better represents its characteristic oak-ash woodland.]]></description>
										<content:encoded><![CDATA[<p>A formal proposal to correct the botanical name of a distinctive forest community could clarify decades of ecological research across northern Spain and southwestern France. The association Polysticho setiferi-Fraxinetum excelsioris has long been used to describe meso-eutrophic, thermophilic woodland in which common oak, Quercus robur, is regularly accompanied by European ash, Fraxinus excelsior, and hazel, Corylus avellana. Although the name is widely established in vegetation maps, monographs, technical reports and administrative documents, the type specimen chosen in 1994 does not represent the vegetation that most later authors understood the association to describe. The proposal therefore asks to retain the familiar name while replacing its type with a conserved neotype collected in Asturias, Spain.</p>
<p>The issue illustrates how the formal type of a named plant community can shape scientific interpretation far beyond the boundaries of taxonomy. Under the International Code of Phytosociological Nomenclature, a type anchors a syntaxonomic name to a particular vegetation record and helps determine which examples should be treated as typical. A poorly chosen type can therefore create a mismatch between a name and the ecological pattern for which it is routinely used. Here, the association was understood by most researchers as an oak-ash forest of moderately nutrient-rich sites, but its selected lectotype describes a stand dominated by beech. The authors argue that conservation of a more representative neotype would resolve the conflict without disturbing the name’s established usage.</p>
<p>The forest community was first recognizable in the vegetation of the Basque Country. In his 1941 monograph, Pierre Allorge described lowland forests dominated by common oak, with regular participation of ash and hazel, scattered deciduous trees, a rich understory and soils that were basic to neutral. Although that account included no formal vegetation plots, its description, geographic range and environmental conditions defined a recognizable forest type in the eastern Cantabrian region. The community occurs broadly in the Atlantic territories between the Adour River in southwestern France and the Nalón River in Asturias, placing its natural distribution across northern Iberia and the neighboring southwestern French coast.</p>
<p>Reinhold von Tüxen and Erich Oberdorfer formally described the association in their 1958 monograph on Spain as Corylo-Fraxinetum cantabricum. They explicitly related it to Allorge’s unit, compared it with the Central European Querco-Carpinetum and noted its geographic relationship to the Irish Corylo-Fraxinetum. Their original table contained two relevés assigned to a typical subassociation. Both had relatively low oak abundance, a circumstance the authors attributed partly to the historical clearance of the best oak stands for farmland. Because common oak was scarce in many of the surveyed sites, the original name emphasized ash rather than oak. The name also included the geographic epithet cantabricum, which later became ineligible under Article 34 of the code.</p>
<p>Rivas-Martínez consequently adopted the replacement name Polysticho setiferi-Fraxinetum excelsioris, drawing on the diagnostic Polystichum setiferum and the name-giving ash. The form first appeared in a 1981 doctoral thesis that used a nomenclatural attribution to Rivas-Martínez. Although that thesis is often cited as the validating publication, it was reproduced as a xerocopy without an ISBN and therefore did not meet the code’s requirements for effective publication. The name was consequently validated incidentally by Díaz and Fernández Prieto in 1994, who also treated Corylo-Fraxinetum cantabricum as a synonym. The accepted full citation thus identifies the earlier 1958 basionym while crediting the valid modern name to the 1994 publication.</p>
<p>The decisive problem arose when Díaz and Fernández Prieto selected a lectotype from the original table in accordance with the second edition of the International Code of Phytosociological Nomenclature. Their choice was relevé 139, one of two plots in the typical subassociation. It was selected because it was the only member of that pair containing any common oak, recorded at low abundance. The same plot was dominated by beech, Fagus sylvatica, however, with a cover value of 4.4 under the relevé scale. That characteristic conflicts with the community’s long-standing interpretation as a forest in which common oak has high frequency and may dominate. Beech is comparatively uncommon in the typical association, making the selected plot an atypical expression of the vegetation rather than a clear anchor for it.</p>
<p>Both plots cited by the original authors have environmental features that help explain their unusual composition. One represents a high-altitude site with above-average rainfall, favoring beech, while the other occupies a humid location containing plants associated with alder riverine forests. Tüxen and Oberdorfer themselves qualified the plots, observing that their species combinations might approximate the type of the association even though the relative abundance of the trees departed from the normal pattern. Later field surveys across Cantabrian territories revealed the more consistent structure of a meso-eutrophic mixed forest with frequent common oak. The proposal maintains that the 1994 lectotype failed to capture this established concept and that selecting it as the type generated interpretive problems for subsequent classification and conservation work.</p>
<p>To correct the mismatch, the authors invoke Article 53 of the fourth edition of the International Code of Phytosociological Nomenclature and request a conserved neotype. Their proposed record comes from Palacio de Meres in Siero, Asturias, at 180 metres above sea level on a north-west-facing slope with a gradient of 10 degrees. The 300-square-metre plot stands on marls, clays and sandstones containing whitish and pinkish Eocene limestones. Recorded on 7 July 2021, the stand has a tree layer dominated by common oak, with holly, sycamore maple, hazel and ash also present. This composition closely reflects the oak-ash structure associated with the name throughout the region.</p>
<p>The understory of the proposed neotype also includes the plants needed to characterize the community more comprehensively. The shrub layer contains blackthorn, spindle, dog rose, elder, wayfaring tree, common privet, evergreen rose and yew. The herb layer is diverse, with ivy, blackberry, false brome, wood sedge, a fern complex, herb-robert, ground ivy, spotted dead-nettle, honeysuckle, Solomon’s seal, soft rush, common nettle, bugle, lady’s fern, pendulous sedge, broad-leaved ragwort, St John’s wort, tormentil, lungwort, primrose, madder, common sorrel, betony, bittersweet, black bryony and violets. The presence of Polystichum setiferum, reflected in the association’s name, is confirmed in the herb layer, while oak remains conspicuous in the canopy.</p>
<p>If accepted, the proposal would preserve Polysticho setiferi-Fraxinetum excelsioris as the operative name while aligning its type with the association’s dominant ecological interpretation. The move is not intended to rename the forest community or redraw its range. Instead, it would correct the nomenclatural anchor used to identify it, reducing the chance that future comparisons, vegetation classifications and habitat assessments will treat a beech-rich exceptional stand as the standard. The case also demonstrates why botanical community names require careful stewardship: scientific continuity can depend on a precise formal connection between a widely used name, its type and the living vegetation it represents.</p>
<p><strong>Subject of Research:</strong> Conservation of the nomenclatural type of an oak-ash forest association in northern Iberia and southwestern France</p>
<p><strong>Article Title:</strong> ﻿Proposal (30) to conserve the name Polysticho setiferi-Fraxinetum excelsioris (Tüxen et Oberdorfer 1958) Rivas-Martínez ex Díaz et Fernández Prieto 1994 with a conserved type</p>
<p><strong>Article References:</strong> Loidi, J., Amigo, J., Bueno, Á., Herrera, M., &amp; Rodríguez-Guitián, M. A. (2022). ﻿Proposal (30) to conserve the name Polysticho setiferi-Fraxinetum excelsioris (Tüxen et Oberdorfer 1958) Rivas-Martínez ex Díaz et Fernández Prieto 1994 with a conserved type. <em>Vegetation Classification and Survey, 3</em>, 187-189. <a href="https://doi.org/10.3897/vcs.86799" rel="noopener noreferrer">https://doi.org/10.3897/vcs.86799</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.3897/VCS.86799" rel="noopener noreferrer">10.3897/VCS.86799</a></p>
<p><strong>Keywords:</strong> phytosociology, plant nomenclature, oak-ash forest, conserved neotype, Quercus robur, Iberian vegetation, Cantabrian forests, International Code of Phytosociological Nomenclature, Proposal, conserve, name, Polysticho</p>
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		<post-id xmlns="com-wordpress:feed-additions:1">315243</post-id>	</item>
		<item>
		<title>Climate Change Could Push Invasive Silver Wattle Into New Temperate Frontiers</title>
		<link>https://scienmag.com/climate-change-could-push-invasive-silver-wattle-into-new-temperate-frontiers/</link>
		
		<dc:creator><![CDATA[Sloane Callahan]]></dc:creator>
		<pubDate>Wed, 30 Sep 2026 23:13:19 +0000</pubDate>
				<category><![CDATA[Earth Science]]></category>
		<category><![CDATA[Acacia dealbata]]></category>
		<category><![CDATA[Acacia dealbata invasive potential]]></category>
		<category><![CDATA[Australian native plants in Europe]]></category>
		<category><![CDATA[Biodiversity Conservation]]></category>
		<category><![CDATA[biological invasions]]></category>
		<category><![CDATA[climate change]]></category>
		<category><![CDATA[climate change impact on invasive trees]]></category>
		<category><![CDATA[climate-driven habitat shift]]></category>
		<category><![CDATA[climatic niche]]></category>
		<category><![CDATA[CMIP6 scenarios]]></category>
		<category><![CDATA[Europe]]></category>
		<category><![CDATA[high emission climate scenarios]]></category>
		<category><![CDATA[invasive alien species]]></category>
		<category><![CDATA[invasive legume ecological impact]]></category>
		<category><![CDATA[Invasive species climate change]]></category>
		<category><![CDATA[invasive species management and policy]]></category>
		<category><![CDATA[invasive tree species Europe]]></category>
		<category><![CDATA[MaxEnt]]></category>
		<category><![CDATA[Quercus robur]]></category>
		<category><![CDATA[Silver Wattle range expansion]]></category>
		<category><![CDATA[species distribution modeling]]></category>
		<category><![CDATA[species distribution models]]></category>
		<category><![CDATA[temperate forest invasion risk]]></category>
		<category><![CDATA[temperate forests]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=220002</guid>

					<description><![CDATA[New global species distribution modelling shows that projected climate change could expand the climatic suitability of the invasive Australian tree Acacia dealbata polewards into temperate European regions, including the British Isles, increasing its overlap with native oak forests.]]></description>
										<content:encoded><![CDATA[<p>An Australian tree with silvery fern-like leaves and a talent for conquest may be preparing to march into some of the world&#8217;s most cherished temperate forests. A new modelling study published in Environmental Monitoring and Assessment suggests that projected climate change could substantially expand the geographical suitability of Acacia dealbata, the silver wattle, pushing its potential range polewards into regions of Europe that have so far remained largely beyond its reach. Using global species distribution models, researchers at the Universidade de Vigo in Spain found that the climatic niche of this invasive legume has already grown by more than 13 percent in recent decades, and that under high-emission scenarios its suitable habitat could stretch as far north as the Atlantic coasts of Ireland and Scotland.</p>
<p>Acacia dealbata is no ordinary newcomer. Native to the temperate coastal zones of south-eastern and south-western Australia and to Tasmania, the species was introduced to Europe in the late 1700s as an ornamental plant and as a source of fuelwood and construction timber. Since then it has become one of the most successful invasive trees on the continent, particularly in the Iberian Peninsula and the Mediterranean basin. It is officially listed as an invasive alien species in Spain and Portugal, and several of its relatives, including Acacia saligna, appear on the European Union&#8217;s list of invasive alien species of Union concern. France and Italy, both hotspots for acacia proliferation, have so far refrained from specific legislation targeting the genus, largely because the cut-flower and perfume industries depend on it.</p>
<p>The secret to the silver wattle&#8217;s success lies in a formidable arsenal of ecological traits. It grows rapidly, shading out native competitors in the race for sunlight. Its extensive root systems deplete soil water, starving neighbouring plants of a scarce resource. It is a generalist in terms of nutrient availability, thriving where fussier species struggle. It resprouts vigorously after disturbance, produces allelopathic leachates that chemically suppress rivals, and fixes atmospheric nitrogen through its leguminous symbiosis, enriching soils in ways that can favour its own kind over native flora adapted to poorer ground. Crucially, it is remarkably resilient to bushfires and elevated atmospheric carbon dioxide, meaning that the very disturbances amplified by climate change may work in its favour rather than against it.</p>
<p>To map where this invader might strike next, the research team, led by Pedro Lago-González, built maximum entropy models, a widely used statistical framework known as MaxEnt that estimates the most uniform probability distribution consistent with known species occurrences. The team compared the climatic niche of Acacia dealbata with that of Quercus robur, the pedunculate oak, a defining species of temperate broadleaf deciduous forests in Europe and western Asia and a representative of habitats highly sensitive to acacia invasion. Occurrence records came from the Global Biodiversity Information Facility, while climate data spanning 1963 to 2023 was drawn from the NCEP/NCAR reanalysis project, with future projections taken from the CESM2 Earth system model under four shared socioeconomic pathways, ranging from the optimistic SSP1-2.6 to the severe SSP5-8.5.</p>
<p>The technical pipeline was deliberately rigorous. Rather than feeding raw climate data into the models, the researchers engineered a physically meaningful set of predictors: mean values representing baseline conditions, annual ranges and seasonality indices capturing periodic variability, and empirical orthogonal function components describing interannual climate variability. Isothermality and daily thermal range were included for temperature, while precipitation was summarised through annual accumulation, seasonality, and monthly extremes. Species occurrence data was cleaned of duplicates and offshore records, spatially thinned at a 25-kilometre radius to counteract uneven sampling, and background points were generated with a global accessibility weighting to mimic sampling bias. The models were trained with fivefold cross-validation and evaluated with area under the curve metrics, achieving values above 0.90, a level of performance consistent with previous acacia distribution studies.</p>
<p>Temperature emerged as the dominant force shaping the silver wattle&#8217;s distribution. Average temperature alone contributed 42 percent of the model in the earlier period and, by permutation importance, 39 percent in the later one, with temperature seasonality also playing a major role. The response curves tell a striking story: suitability for Acacia dealbata climbs steadily as average temperature rises, peaking between roughly 13 and 20 degrees Celsius before collapsing near 25 degrees. The oak, by contrast, prefers cooler conditions, with its modelled optimum centred near 8 to 9 degrees Celsius. The two species share a remarkable 9.9 million square kilometres of territory, mostly in the mid-latitudes, yet their climatic profiles differ significantly for nearly every variable. Acacia tolerates a wider amplitude of daily temperature range and endures more contrasting precipitation regimes, including drier minima and greater precipitation seasonality, than the oak.</p>
<p>The overlap between the two niches is quantified through Schoener&#8217;s D and Hellinger&#8217;s I, indices that measure how closely two probability distributions coincide across a landscape. Both indices rose between the two historical periods, with Schoener&#8217;s D climbing from 0.26 to 0.34 and Hellinger&#8217;s I from 0.55 to 0.61. The principal hotspot of this overlap is western Europe, especially northern Spain and France, where oak forests and silver wattle already coexist uneasily. Secondary hotspots include the south-eastern Australian coast, New Zealand, and stretches of the Pacific coast of the Americas. Notably, the spatial pattern of overlap changed little between periods; rather, it intensified in the very places where it was already established, suggesting a concentration of conflict rather than a wholesale relocation.</p>
<p>The future projections are where the study delivers its most consequential warning. Under the mildest scenario, SSP1-2.6, silver wattle suitability in Europe remains confined to a few Atlantic coastal fringes of the south-west. But as radiative forcing increases, so does the European footprint of the species. Under SSP2-4.5 and SSP3-7.0, suitability expands markedly across Mediterranean Europe, with the probability of occurrence increasing by more than 60 percent in some Mediterranean areas. Under the most severe scenario, SSP5-8.5, the species&#8217; climatic niche shifts dramatically northwards, reaching the British Isles, with the Irish Atlantic coast highlighted as particularly suitable. Meanwhile, oak suitability behaves differently: rather than simply declining with forcing, it migrates towards the poles, concentrating under high-emission conditions along Scandinavian Atlantic coasts and the northernmost territories of Ireland and Scotland. Niche overlap between the two species generally increased with radiative forcing, with the strongest overlap under SSP5-8.5 concentrated over north-western Europe and the mid-latitude Pacific coast of South America.</p>
<p>The authors are careful to spell out the limitations of their approach. MaxEnt assumes that species spread to an equilibrium state consistent with the climate, which is rarely true in practice, and the model considers only climatic variables, omitting soil characteristics, land use, biotic interactions, and the socioeconomic forces that drive introductions. The relatively coarse climate grid, interpolated to a finer resolution, may smooth environmental gradients and inflate suitable areas. Nor can the model distinguish between areas that are climatically suitable but not yet reached by the species and areas that become newly suitable under climate change. Interestingly, the study also found that acacia suitability decreased in some regions, such as southern Brazil, for reasons that neither climate shifts nor human intervention readily explain, a puzzle the authors flag for future research.</p>
<p>Nevertheless, the management implications are clear and urgent. The researchers argue that invasion prevention should look not only at where Acacia dealbata currently thrives but at where it could thrive tomorrow. Countries such as France, the United Kingdom, Italy, and Croatia cultivate the species ornamentally, and the study suggests these nations could face growing establishment risk, particularly under stronger warming. Rather than outright bans, which the authors acknowledge may be excessive, they advocate early surveillance programmes, noting that the species can already be detected by remote sensing combined with machine learning algorithms, a cost-effective route to operational monitoring. Riparian ecosystems deserve particular attention, as the species aggregates along watercourses that serve as dispersal corridors. Rapid response plans, they argue, should be designed now for uninvaded areas that may become vulnerable as temperate zones shift. In a warming world, the front line of the battle against biological invasions is moving north, and the silver wattle, with its fire-forged resilience and nitrogen-fixing ambition, is following the heat.</p>
<p><strong>Subject of Research:</strong> Projected effects of climate change on the global climatic niche and potential distribution of the invasive tree Acacia dealbata in temperate forests</p>
<p><strong>Article Title:</strong> Projected climate change could expand the geographical suitability of Acacia dealbata into new temperate areas</p>
<p><strong>Article References:</strong> Lago-González, P., Acuña-Alonso, C., &amp; Álvarez, X. (2026). Projected climate change could expand the geographical suitability of Acacia dealbata into new temperate areas. <em>Environmental Monitoring and Assessment, 198</em>(10), Article 1131. <a href="https://doi.org/10.1007/s10661-026-15951-5" rel="noopener noreferrer">https://doi.org/10.1007/s10661-026-15951-5</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.1007/s10661-026-15951-5" rel="noopener noreferrer">10.1007/s10661-026-15951-5</a></p>
<p><strong>Keywords:</strong> Acacia dealbata, invasive alien species, species distribution models, MaxEnt, climate change, Quercus robur, temperate forests, climatic niche, CMIP6 scenarios, biological invasions, Europe, biodiversity conservation</p>
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		<title>Climate Change Could Rewrite the Map of Iberian Oak Forests by Century&#8217;s End</title>
		<link>https://scienmag.com/climate-change-could-rewrite-the-map-of-iberian-oak-forests-by-centurys-end/</link>
		
		<dc:creator><![CDATA[Sloane Callahan]]></dc:creator>
		<pubDate>Wed, 30 Sep 2026 19:58:27 +0000</pubDate>
				<category><![CDATA[Climate]]></category>
		<category><![CDATA[climate change]]></category>
		<category><![CDATA[Climate Change Impact]]></category>
		<category><![CDATA[climate-driven forest composition]]></category>
		<category><![CDATA[conservation]]></category>
		<category><![CDATA[cork oak decline]]></category>
		<category><![CDATA[drought-tolerant oak species]]></category>
		<category><![CDATA[forest management]]></category>
		<category><![CDATA[forest species redistribution]]></category>
		<category><![CDATA[habitat suitability]]></category>
		<category><![CDATA[Iberian oak forests]]></category>
		<category><![CDATA[Iberian Peninsula]]></category>
		<category><![CDATA[Iberian Peninsula landscape change]]></category>
		<category><![CDATA[Mediterranean climate warming]]></category>
		<category><![CDATA[Mediterranean forests]]></category>
		<category><![CDATA[moisture-dependent oak species]]></category>
		<category><![CDATA[oak forests]]></category>
		<category><![CDATA[pedunculate oak habitat shift]]></category>
		<category><![CDATA[Pyrenean oak adaptation]]></category>
		<category><![CDATA[Quercus pyrenaica]]></category>
		<category><![CDATA[Quercus robur]]></category>
		<category><![CDATA[Quercus suber]]></category>
		<category><![CDATA[spatial forest ecology]]></category>
		<category><![CDATA[species distribution models]]></category>
		<category><![CDATA[species turnover]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=218726</guid>

					<description><![CDATA[High-resolution climate modelling projects that drought-tolerant cork oak will progressively replace Pyrenean and pedunculate oaks across much of the Iberian Peninsula by 2100, reshaping forest composition and conservation planning.]]></description>
										<content:encoded><![CDATA[<p>The great oak forests of the Iberian Peninsula, which have anchored western Iberia&#8217;s landscapes for millennia, may be quietly changing hands. A new open-access study published in Discover Conservation projects that as the Mediterranean climate warms and dries, drought-tolerant oak species will progressively replace their moisture-dependent relatives across large swaths of Spain and Portugal. The research, led by Isabel Passos of the Polytechnic Institute of Castelo Branco together with colleagues at the University of Coimbra, the University of Porto and partner institutions, offers one of the most detailed spatial pictures yet of how the dominant trees of Iberian forests could be reshuffled over the coming decades.</p>
<p>The team focused on three oak species that dominate the climax forests of acidic substrates across the peninsula: cork oak (Quercus suber), Pyrenean oak (Quercus pyrenaica) and pedunculate oak (Quercus robur). These species sit at different points along a moisture gradient. Pedunculate oak, a temperate and humidity-loving species, thrives in the cool Atlantic north. Pyrenean oak, a marcescent species that holds its withered leaves through winter, occupies a transitional submediterranean zone. Cork oak, the iconic evergreen of Mediterranean silviculture, tolerates pronounced summer drought. Because the three species often coexist in the same landscapes, distributed along gradients from rocky ridge tops to moist valley bottoms, the researchers reasoned that climate change could trigger a domino effect: as each species retreats from its drier margins, a more drought-adapted congener may move in to take its place.</p>
<p>To test this idea, the researchers built high-resolution species distribution models at a one-square-kilometre resolution, integrating nearly a quarter of a million cleaned occurrence records from GBIF, national biodiversity databases and expert-curated sources. For pedunculate oak, the team applied a spatial thinning procedure that reduced more than 205,000 records to about 27,000, mitigating oversampling while preserving the species&#8217; environmental coverage. The models combined nineteen bioclimatic indices from the CHELSA dataset with soil pH, soil texture, a Topographic Ruggedness Index and a Topographic Wetness Index, all chosen through hypothesis-driven screening that excluded collinear predictors.</p>
<p>The modelling framework was an ensemble approach implemented in the biomod2 package in R, combining eight techniques ranging from generalized linear models and generalized additive models to random forests, artificial neural networks and maximum entropy. Each model was validated over ten rounds of cross-validation, and only algorithms exceeding a True Skill Statistic threshold of 0.7 were averaged into the final ensembles. Performance was strong across the board: TSS values exceeded 0.83 and AUC scores surpassed 0.97 for all three species, with cork oak models performing best. Future projections drew on five general circulation models selected for their strong performance over Europe, run under two Shared Socioeconomic Pathways: an intermediate SSP3-7.0 scenario and a pessimistic SSP5-8.5 scenario, for the mid-century period 2041 to 2070 and the late-century period 2071 to 2100.</p>
<p>The environmental variables that best explained each species&#8217; current distribution revealed their distinct ecological thresholds. For pedunculate oak, the minimum temperature of the coldest month was the dominant predictor, reflecting its tolerance of subzero winters, followed by topographic ruggedness and precipitation of the warmest quarter. Pyrenean oak&#8217;s distribution hinged on annual precipitation and warm-season rainfall together with soil pH, underscoring its dependence on water availability during the hot, dry summer. Cork oak, by contrast, was governed primarily by soil pH and mean annual temperature, favouring sites where winter minima stay above freezing. All three species are strictly silicicole, confined to acidic substrates, which means that climatically suitable areas on limestone soils will remain off-limits no matter how the climate shifts.</p>
<p>The projected trajectories diverge sharply. Pedunculate oak&#8217;s current range is expected to remain largely stable, with between 73 and 84 percent of its present suitable area persisting across scenarios, though its total suitable area declines slightly as losses outweigh gains. Cork oak emerges as the clear winner: its suitable range expands in every scenario and time frame, gaining between 32 and 44 percent of new territory, pushing northward and inland, with potential altitudinal advances reaching as far as the Pyrenees, while losing almost nothing at its southern edge. Pyrenean oak fares worst. Its total suitable area shrinks in all scenarios, with losses of up to nearly 60 percent of its current range concentrated in the southern and inland parts of the peninsula, and only limited compensatory gains at higher elevations.</p>
<p>When the researchers overlaid the range dynamics of different species, the turnover patterns became strikingly clear. Wherever one species loses suitability while another gains or holds steady in the same grid cells, a potential replacement is flagged. The dominant signal is a turnover from Pyrenean oak to cork oak, projected across roughly 20 to 47 percent of Pyrenean oak&#8217;s currently suitable range depending on the scenario, intensifying toward the end of the century and under harsher emissions. This replacement is expected to begin at the species&#8217; southern fringes and spread into the interior. A smaller turnover, from pedunculate oak to Pyrenean oak, is projected across about 5 to 8 percent of the former&#8217;s range, mostly in low-altitude inland areas at the southern edge of its distribution. In some coastal zones of western and northeastern Iberia, cork oak may ultimately replace both of the other species where they both become unsuitable.</p>
<p>A crucial dimension of the study is its analysis of protected areas. Between a quarter and nearly half of the projected turnover zones fall inside classified conservation sites, including Natura 2000 areas designated under the European Union&#8217;s Habitats Directive, national parks and nature reserves. The turnover from Pyrenean oak to cork oak carries a direct policy consequence: it implies a shift from habitat 9230, the Galicio-Portuguese oak woods, to habitat 9330, cork oak forests, within sites whose management plans were written for the habitats of the past. The researchers argue that conservation targets in these sites will need periodic revision to maintain habitat continuity under changing climates, and that protected areas can serve as demonstration cases for adaptive management on the privately owned lands that dominate the Portuguese landscape.</p>
<p>The authors are careful to frame these projections as shifts in potential climatic and edaphic suitability rather than deterministic predictions of stand-level replacement. The models do not explicitly simulate dispersal, disturbance regimes or biotic interactions, and oak species are notoriously slow to migrate relative to the pace of climate change. Yet the convergent trends across multiple climate models and scenarios lend weight to the central inference: that a gradual Mediterraneanization of the Iberian landscape is underway, marked by longer summer dry periods and reduced annual precipitation, in which drought-adapted oaks progressively occupy the space vacated by their moisture-dependent relatives.</p>
<p>The practical implications reach deep into forestry. The researchers recommend protecting natural regeneration of the species likely to dominate in the future, since cork oak individuals already occur near Pyrenean oak stands on rocky outcrops and within forests. Where natural regeneration is insufficient, they point to seed sowing and planting techniques, including autumn sowing to maximize root development before summer drought, selection of larger acorns, protection from seed predators such as wild boar, and the use of large containers to avoid root deformation. They also advocate multi-provenance strategies that draw reproductive material from southern or low-altitude populations already adapted to drier conditions, combined with mixed-species stands to hedge risk. If guided by such adaptive management, the authors conclude, species turnover need not spell the loss of Iberian forests; it may instead be the mechanism by which they retain canopy cover, ecological function and resilience through a century of rapid environmental change.</p>
<p><strong>Subject of Research:</strong> Projected climate-driven species turnover among Iberian oak forests</p>
<p><strong>Article Title:</strong> Exploring turnover dynamics in Iberian Oak forests under climate change scenarios</p>
<p><strong>Article References:</strong> Passos, I., Figueiredo, A., Gonçalves, J., Ribeiro, M. M., &amp; Vila-Viçosa, C. (2026). Exploring turnover dynamics in Iberian Oak forests under climate change scenarios. <em>Discover Conservation, 3</em>(1), Article 14. <a href="https://doi.org/10.1007/s44353-026-00084-0" rel="noopener noreferrer">https://doi.org/10.1007/s44353-026-00084-0</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.1007/s44353-026-00084-0" rel="noopener noreferrer">10.1007/s44353-026-00084-0</a></p>
<p><strong>Keywords:</strong> climate change, oak forests, Quercus suber, Quercus pyrenaica, Quercus robur, species distribution models, species turnover, Iberian Peninsula, Mediterranean forests, forest management, conservation, habitat suitability</p>
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