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	<title>macroecology &#8211; Science</title>
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	<title>macroecology &#8211; Science</title>
	<link>https://scienmag.com</link>
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		<title>Dynamic Land-Use Model Reveals Extinction Risk May Spike Abruptly, and Protected Areas Can Bend the Curve</title>
		<link>https://scienmag.com/dynamic-land-use-model-reveals-extinction-risk-may-spike-abruptly-and-protected-areas-can-bend-the-curve/</link>
		
		<dc:creator><![CDATA[Margaret Porter]]></dc:creator>
		<pubDate>Sat, 03 Oct 2026 01:38:44 +0000</pubDate>
				<category><![CDATA[Biology]]></category>
		<category><![CDATA[abrupt extinction events]]></category>
		<category><![CDATA[biodiversity]]></category>
		<category><![CDATA[conservation]]></category>
		<category><![CDATA[conservation strategies for protected areas]]></category>
		<category><![CDATA[delayed extinction effects]]></category>
		<category><![CDATA[ecological modeling of land-use impacts]]></category>
		<category><![CDATA[endemics-area relationship]]></category>
		<category><![CDATA[extinction debt]]></category>
		<category><![CDATA[extinction risk]]></category>
		<category><![CDATA[Fisher-KPP model]]></category>
		<category><![CDATA[habitat destruction and species loss]]></category>
		<category><![CDATA[habitat fragmentation]]></category>
		<category><![CDATA[habitat fragmentation and merging]]></category>
		<category><![CDATA[land use change]]></category>
		<category><![CDATA[land-use change impact on biodiversity]]></category>
		<category><![CDATA[macroecological land conversion patterns]]></category>
		<category><![CDATA[macroecology]]></category>
		<category><![CDATA[nonlinear extinction dynamics]]></category>
		<category><![CDATA[protected areas]]></category>
		<category><![CDATA[spatial modeling]]></category>
		<category><![CDATA[spatial spread of land development]]></category>
		<category><![CDATA[species extinction risk modeling]]></category>
		<category><![CDATA[species-area and endemics-area relationships]]></category>
		<category><![CDATA[species-area relationship]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=230043</guid>

					<description><![CDATA[A new spatially explicit model shows that simultaneous, merging land-use events make species loss accelerate abruptly at later conversion stages, while early establishment of protected areas can significantly bend the extinction curve.]]></description>
										<content:encoded><![CDATA[<p>Every estimate of how many species humanity will lose to deforestation, urbanization, and agricultural expansion rests on a quiet mathematical assumption: that habitat disappears in a simple, predictable way. A new modeling study published in Ecology and Evolution argues that this assumption is precisely where many extinction projections go wrong. By coupling a classic equation of population growth with a macroecological framework for species ranges, researchers have shown that when land conversion happens the way it actually happens on Earth—starting in many places at once, spreading outward, and merging as patches collide—the shape of the extinction curve changes fundamentally. Species loss appears to be delayed, then arrives all at once, like a dam that holds until it suddenly does not.</p>
<p>The study, led by Nao Takashina with Buntarou Kusumoto, tackles a long-standing tension in conservation science. The workhorses of extinction forecasting are the species-area relationship (SAR) and its mirror image, the endemics-area relationship (EAR). The SAR tallies how many species occupy a given area of habitat; the EAR counts how many species are found nowhere else, and therefore vanish the moment their entire range is destroyed. Both have been applied at scales from single forest plots to the entire planet, and both are embedded in the machinery of international biodiversity targets. But both were built on simplified pictures of habitat loss: a single block of conversion expanding in one direction, or a static level of fragmentation frozen in time.</p>
<p>Real landscapes are messier. A new field is cleared here, a road pushed through there, a suburb swells at the edge of a city. Converted patches emerge simultaneously across a region, expand at different speeds, and coalesce when they meet, so the degree of fragmentation is not fixed but evolves continuously. To capture this, the team turned to the Fisher–KPP equation, a reaction–diffusion model originally devised to describe the spread of advantageous genes. In their formulation, land-use intensity grows logistically at each location and diffuses across space, with separate diffusion coefficients allowing expansion to run faster east–west than north–south. Crucially, the model includes the conventional single-origin scenario as a limiting case: when no new conversion events occur, it collapses back to the standard sampling-area setting that underlies traditional estimates.</p>
<p>On the ecological side, the researchers generated virtual species assemblages grounded in well-established macroecological patterns. Species ranges were placed randomly or arranged along a latitudinal gradient in richness, and range sizes were drawn from a beta distribution tuned to reproduce the left-skewed range-size frequency distributions observed empirically across taxa from primates to beetles. The team then ran hundreds of simulations, overlaying dynamic land conversion onto these species maps and recording, at every time step, how many species had lost their entire geographic range. Alternative extinction criteria—loss of 90 or 95 percent of a range, and the SAR-based rule that any overlap with conversion spells extinction—were tested for comparison.</p>
<p>The central result is counterintuitive and, in its implications, sobering. When land conversion emerged frequently and in many places at once, species loss per unit of converted area was lower in the early stages than under a single expanding conversion front. Dispersed patches are simply less likely to swallow a species&#8217; entire range early on. But as conversion progressed, the endemics-area relationship steepened sharply, producing a much sharper rise in extinctions at later stages than the single-origin scenario ever predicts. In other words, fragmented, multi-site land use does not soften the extinction blow—it postpones it and then concentrates it.</p>
<p>There is a second, more insidious twist. Area-based extinction curves have no clock in them; they relate species loss to the proportion of land converted, not to time. Yet the simulations showed that when new conversion events emerge frequently, a given proportion of converted area is reached far faster than when conversion spreads from a single origin. An apparent delay in area-based species loss therefore does not imply a temporal delay in biodiversity loss. The authors point to the finding that only about 23 percent of terrestrial areas remain relatively wild, suggesting many landscapes may already be entering the late conversion stages where species loss accelerates most abruptly.</p>
<p>Against this backdrop, the study delivers a message of cautious hope about protected areas. When the researchers designated protected cells covering 5 percent of the simulated region—selected from the highest-richness, still-unconverted grids after 20 or 40 percent of the land had been converted—the extinction curve bent visibly downward and its slope declined. Protected cells acted as internal barriers that land-use intensity could not cross, buffering the accumulation of habitat loss. And timing mattered: introducing protected areas earlier, when less land had been converted, saved more species than the same total extent designated later, particularly in the single-origin scenario where early losses accumulate fastest.</p>
<p>The analysis of protected-area geometry added a further layer. Using the pair correlation function, a tool from spatial statistics that measures how frequently protected cells sit at given distances from one another, the team showed that the realized configuration of protected areas was strongly shaped by the underlying land-use regime. Under frequent, dispersed conversion, earlier designation produced more strongly clustered reserves; under contiguous expansion, the clustering differences between early and late designation shifted with distance. When the model was extended to density-dependent land use—where expanding patches interact and total converted area can even shrink—the broad conclusions held, though the extinction curves became noisier because the same converted-area value can recur at multiple time points.</p>
<p>The authors are careful about the limits of their claims. The endemics-area framework assumes immediate extinction upon complete range loss, but alternative criteria introduce the well-known problem of extinction debt: species can persist for decades or even centuries after their habitat is largely destroyed, with documented debts spanning from a few years to 570 years. Under such delayed criteria, a small network of protected areas may prevent immediate extinctions in the short term without suppressing the long-run debt. Sufficiently large protected areas, the study suggests, are needed to bend the extinction curve permanently, not merely postpone it. The work also stops short of the richer reality of socio-ecological landscapes, where traditional agriculture sustains biodiversity and other effective area-based conservation measures complement formal reserves.</p>
<p>Even with those caveats, the study lands at a politically charged moment. The Kunming-Montreal Global Biodiversity Framework commits nations to rapid expansion of area-based conservation, and previous research has warned that delays in establishing protected areas—sometimes justified by the hope of better information—create missed conservation opportunities that can never be recovered. This new modeling effort provides theoretical backing for that warning: because dynamic land use can accelerate the pace of conversion in real time even while appearing to delay species loss on paper, every year of postponement compounds the risk. The extinction curve, the study suggests, is not a gentle slope we can read far ahead. It is a curve that flattens, lulls, and then turns sharply upward—and the window in which protected areas can bend it is open now, and closing.</p>
<p><strong>Subject of Research:</strong> Modeling species extinction risk under dynamic spatiotemporal land-use processes and the conservation role of protected areas</p>
<p><strong>Article Title:</strong> Species Extinction Curves Under Emergent Spatiotemporal Land‐Use Processes and the Role of Protected Areas</p>
<p><strong>Article References:</strong> Takashina, N., &amp; Kusumoto, B. (2026). Species Extinction Curves Under Emergent Spatiotemporal Land‐Use Processes and the Role of Protected Areas. <em>Ecology and Evolution, 16</em>(10), Article e74433. <a href="https://doi.org/10.1002/ece3.74433" rel="noopener noreferrer">https://doi.org/10.1002/ece3.74433</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.1002/ece3.74433" rel="noopener noreferrer">10.1002/ece3.74433</a></p>
<p><strong>Keywords:</strong> biodiversity, extinction risk, land-use change, species-area relationship, endemics-area relationship, protected areas, habitat fragmentation, Fisher-KPP model, macroecology, conservation, extinction debt, spatial modeling</p>
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		<post-id xmlns="com-wordpress:feed-additions:1">230043</post-id>	</item>
		<item>
		<title>Counting Fish the Wrong Way: How Survey Methods Reshape What We Think Coral Reefs Tell Us</title>
		<link>https://scienmag.com/counting-fish-the-wrong-way-how-survey-methods-reshape-what-we-think-coral-reefs-tell-us/</link>
		
		<dc:creator><![CDATA[Margaret Porter]]></dc:creator>
		<pubDate>Fri, 25 Sep 2026 01:07:30 +0000</pubDate>
				<category><![CDATA[Earth Science]]></category>
		<category><![CDATA[belt transects]]></category>
		<category><![CDATA[biomass estimation]]></category>
		<category><![CDATA[challenges in large-scale reef fish data collection]]></category>
		<category><![CDATA[coral reef biodiversity monitoring]]></category>
		<category><![CDATA[coral reef ecosystem health assessment]]></category>
		<category><![CDATA[coral reef fish]]></category>
		<category><![CDATA[coral reef fish survey methods]]></category>
		<category><![CDATA[diver effect]]></category>
		<category><![CDATA[ecological monitoring]]></category>
		<category><![CDATA[effects of diver movement on fish counts]]></category>
		<category><![CDATA[Great Barrier Reef]]></category>
		<category><![CDATA[Great Barrier Reef fish survey accuracy]]></category>
		<category><![CDATA[impact of survey technique on ecological data]]></category>
		<category><![CDATA[implications of survey methods for reef conservation]]></category>
		<category><![CDATA[influence of survey duration on fish detection]]></category>
		<category><![CDATA[macroecology]]></category>
		<category><![CDATA[methodological biases in reef fish censuses]]></category>
		<category><![CDATA[point counts]]></category>
		<category><![CDATA[reef fish population assessment]]></category>
		<category><![CDATA[size spectrum]]></category>
		<category><![CDATA[species richness]]></category>
		<category><![CDATA[stationary point counts vs belt transects]]></category>
		<category><![CDATA[survey methodology]]></category>
		<category><![CDATA[underwater visual census]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=213723</guid>

					<description><![CDATA[A new Great Barrier Reef study shows that point counts and belt transects, the two most common coral reef fish census methods, produce fundamentally different estimates of abundance, biomass and community energy dynamics, warning that combining incompatible survey data can distort macroecological conclusions.]]></description>
										<content:encoded><![CDATA[<p>On a coral reef, the difference between seeing a thriving ecosystem and a collapsing one can come down to how long a diver holds still. That is the startling implication of a new study published in the journal Coral Reefs, in which researchers from James Cook University, the University of Sydney and partner institutions systematically compared the two most widely used techniques for counting reef fishes: stationary point counts and belt transects. Their conclusion is uncomfortable for a field increasingly reliant on massive, stitched-together datasets. The method a scientist chooses does not merely add a little noise to the numbers. It can produce fundamentally different ecological stories about the very same patch of reef.</p>
<p>The research team, led by Helen Yan, conducted their experiment on two fringing reef systems in the central Great Barrier Reef: Pioneer Bay on Orpheus Island, a sheltered no-take scientific research zone, and Indigo Bay on Fantome Island, a semi-exposed area open to most forms of recreational fishing. Separated by roughly ten kilometres, the two bays host distinct benthic and fish assemblages, making them ideal natural laboratories for testing whether census methods behave consistently across different communities. Between 11 and 17 February 2023, four trained observers surveyed fish larger than ten centimetres in total length, spanning eighteen reef fish families, with individuals identified to species, counted, and assigned to five-centimetre size bins.</p>
<p>The experimental design was deliberately rigorous. Each sampling block, performed by a single diver, comprised five surveys: an instantaneous one-minute point count, a continuous ten-minute point count, and belt transects of twenty, thirty and fifty metres, all using a five-metre-wide survey area. Point counts and transects within a block were conducted on non-overlapping reef areas to prevent the disturbance caused by one method from contaminating the other, and the order of methods was randomised to balance systematic diver effects. In total, the team completed 46 blocks on Orpheus Island and 48 on Fantome Island, with transect tape laid as the diver counted, a technique designed to minimise the fear response that reef fishes show toward approaching divers.</p>
<p>The results were striking. Point counts produced the most extreme estimates of abundance, biomass and species richness of any method tested. Instantaneous point counts recorded the lowest values, with median abundance estimates of just 0.16 individuals per square metre and standing biomass of 32.3 grams per square metre, while continuous ten-minute point counts recorded the highest, at 0.54 individuals and 93.1 grams per square metre. Transects of different lengths, by contrast, produced remarkably similar estimates, with abundance values clustering between 0.26 and 0.30 individuals per square metre regardless of whether the diver swam twenty, thirty or fifty metres. The discrepancy between the two point count variants points to a bias that is rarely recorded, let alone standardised, in reef fish censuses: total survey time. The longer a diver watches a patch of reef, the more fish swim into view, inflating counts that are then divided by area and presented as density.</p>
<p>But the deeper problem lay in what the methods missed, not just what they counted. Using size spectrum analyses, which examine how biomass is distributed across body size classes in a manner analogous to trophic pyramids, the researchers found that both point count methods completely failed to record the largest fishes on the reef. The reason is almost certainly the diver effect. A point count requires the diver to descend into or swim through the survey area and then remain at its centre, meaning every fish counted is within a small radius of a rotating, breathing, bubble-emitting human. Far from being a passive observer, the diver is a perceived predator, and wary large fishes simply vanish. Previous research has shown that some reef fish communities require upwards of three hours to return to their original densities after a diver passes, so it is unsurprising that even a ten-minute wait failed to bring big fish back into view.</p>
<p>The consequences of these size-based biases ripple directly into ecological interpretation. On Fantome Island, the instantaneous point count produced a size spectrum slope statistically indistinguishable from zero, a flat profile typically read as a sign of an inverted trophic structure, the kind of pattern associated with disrupted energy flows or external nutrient subsidies. Yet every other survey method produced clearly negative slopes, the expected bottom-heavy signature of a healthy size-structured community. In other words, one of the most common census techniques, applied for just one minute, would have led ecologists to conclude that the reef&#8217;s energetic architecture was fundamentally distorted when, according to all other methods, it was not. The 50-metre transect was the only technique that consistently captured the entire range of fish body sizes detected across both islands, and it also produced the least variable community composition in multivariate analyses.</p>
<p>The study also quantified how much replication any method requires. By repeatedly subsampling their data and measuring the standard error of estimates, the researchers found that every technique needed at least 31 to 36 samples to reach stable precision, defined as estimates within ten percent of the asymptotic value. This threshold matters because many monitoring programs operate with far fewer replicates per site, meaning their estimates may be too imprecise to detect real ecological change. Even the best-performing method, the 50-metre transect, has limits: highly mobile giants such as reef sharks and the bumphead parrotfish Bolbometopon muricatum are so rare and wide-ranging that transects hundreds of metres long would be needed to quantify their densities reliably.</p>
<p>These findings land at a delicate moment for reef science. Coral reefs are transforming under the pressure of climate change, and researchers are racing to assemble macroecological datasets that combine surveys from disparate sources, different organisations and sometimes different decades. Some of the world&#8217;s largest monitoring programs, including the United States National Oceanic and Atmospheric Administration&#8217;s National Coral Reef Monitoring Program and the Australian Institute of Marine Science&#8217;s Long-Term Monitoring Program on the Great Barrier Reef, each rely on their own protocols. The new study shows that pooling such data without accounting for methodological bias risks amplifying artefacts to continental scales, mistaking the fingerprint of a survey technique for a genuine demographic or ecological process. Statistical corrections and detection modelling may help, but the authors caution that when effect sizes are as large as those documented here, even sophisticated analytical tools are unlikely to fully separate methodological bias from real biology.</p>
<p>Fishing pressure adds another layer of complexity. Fishes in heavily fished areas tend to be warier and exhibit greater flight-initiation distances from divers, a well-documented behavioural response. Consistent with this, the maximum fish size recorded by point counts on fished Fantome Island was smaller than on the protected Orpheus Island, suggesting that the size bias of point counts is not fixed but worsens along gradients of human disturbance. A global dataset mixing surveys from pristine reserves and heavily exploited reefs could therefore encode systematically different biases in different places, further muddying macroecological inference.</p>
<p>The authors&#8217; prescription is straightforward, if demanding: adopt uniform survey methodologies, use at least 30 replicates of a minimum 50-metre transect per site, and treat survey time as a standardised variable rather than an afterthought. In an era of big data, they argue, more data is not necessarily better. A smaller dataset collected consistently, with biases that are at least uniform and therefore quantifiable, will yield far more robust conclusions than a sprawling patchwork of incompatible counts. For a field whose findings feed directly into conservation policy, the message is that how we count fish determines not just the numbers we get, but the reefs we think we are saving.</p>
<p><strong>Subject of Research:</strong> Methodological biases in underwater visual census techniques for coral reef fish community surveys</p>
<p><strong>Article Title:</strong> Common census methods can lead to fundamentally different ecological interpretations of coral reef fish communities</p>
<p><strong>Article References:</strong> Yan, H. F., Crisp, S. K., Bellwood, D. R., Siqueira, A. C., &amp; Tebbett, S. B. (2026). Common census methods can lead to fundamentally different ecological interpretations of coral reef fish communities. <em>Coral Reefs</em>. <a href="https://doi.org/10.1007/s00338-026-02959-z" rel="noopener noreferrer">https://doi.org/10.1007/s00338-026-02959-z</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.1007/s00338-026-02959-z" rel="noopener noreferrer">10.1007/s00338-026-02959-z</a></p>
<p><strong>Keywords:</strong> coral reef fish, underwater visual census, point counts, belt transects, size spectrum, diver effect, Great Barrier Reef, survey methodology, macroecology, biomass estimation, species richness, ecological monitoring</p>
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