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	<title>tidal inlets &#8211; Science</title>
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	<title>tidal inlets &#8211; Science</title>
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		<title>Five Years After Sandy, Barrier Islands Still Haven&#8217;t Recovered Their Lost Sand</title>
		<link>https://scienmag.com/five-years-after-sandy-barrier-islands-still-havent-recovered-their-lost-sand/</link>
		
		<dc:creator><![CDATA[Violet Maxwell]]></dc:creator>
		<pubDate>Sun, 11 Oct 2026 16:12:34 +0000</pubDate>
				<category><![CDATA[Earth Science]]></category>
		<category><![CDATA[barrier island geomorphology]]></category>
		<category><![CDATA[barrier island recovery]]></category>
		<category><![CDATA[barrier islands]]></category>
		<category><![CDATA[beach nourishment]]></category>
		<category><![CDATA[climate change and storm effects on coastlines]]></category>
		<category><![CDATA[coastal erosion]]></category>
		<category><![CDATA[coastal geomorphology]]></category>
		<category><![CDATA[dune flattening]]></category>
		<category><![CDATA[Fire Island]]></category>
		<category><![CDATA[human intervention in shoreline restoration]]></category>
		<category><![CDATA[Hurricane Sandy]]></category>
		<category><![CDATA[Hurricane Sandy impact]]></category>
		<category><![CDATA[long-term coastal monitoring]]></category>
		<category><![CDATA[marine and coastal science]]></category>
		<category><![CDATA[Nature Communications.]]></category>
		<category><![CDATA[overwash]]></category>
		<category><![CDATA[post-storm recovery]]></category>
		<category><![CDATA[sand nourishment effectiveness]]></category>
		<category><![CDATA[sea level rise]]></category>
		<category><![CDATA[sediment flux]]></category>
		<category><![CDATA[sediment redistribution]]></category>
		<category><![CDATA[shoreface]]></category>
		<category><![CDATA[shoreline change patterns]]></category>
		<category><![CDATA[tidal inlets]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=262610</guid>

					<description><![CDATA[A five-year sediment budget of Fire Island after Hurricane Sandy reveals that barrier island geometry, not overwash alone, controls how storms redistribute sand and why recovery remains incomplete even with human intervention.]]></description>
										<content:encoded><![CDATA[<p>When Hurricane Sandy slammed into Fire Island, New York, in October 2012, it tore breaches through the barrier island, flattened dunes, and redistributed enormous volumes of sand across the coastal landscape. What happened next, over nearly five years of careful measurement, has surprised even the scientists who study these fragile landforms for a living. A new study published in Nature Communications shows that the island did not simply heal itself after the storm. Instead, sediment moved in patterns dictated by the island&#8217;s underlying geometry, and despite millions of cubic meters of human-placed sand, the barrier never fully recovered. The findings carry sobering implications for the roughly ten percent of open-ocean coastlines worldwide that are fronted by barrier islands, many of which shelter dense human development.</p>
<p>The research team, led by Jennifer Miselis of the U.S. Geological Survey&#8217;s St. Petersburg Coastal and Marine Science Center, assembled an unusually complete picture of a barrier island in motion. Combining three topographic lidar surveys and three bathymetric surveys collected between 2012 and 2018, they tracked sediment volume changes across every sandy environment of the island: the back-barrier lagoon side, the dunes, the beach, the inner shoreface, and the outer shoreface extending to average depths of about 8.6 meters. This shoreface-inclusive perspective is rare. Most post-storm studies stop at the waterline, leaving the submarine half of the sediment budget invisible, and models of long-term barrier behavior have long suffered for it.</p>
<p>Fire Island proved an ideal natural laboratory because it is not a uniform strip of sand. The 51-kilometer island is divided into four geomorphic zones representing distinct evolutionary states: a transgressive eastern zone that has migrated landward over centuries, two zones that prograded historically or geologically seaward, and an elongational western zone that has grown along the direction of net longshore sediment transport. The team focused on six predominantly natural areas of interest, each longer than a kilometer, to minimize the confounding effects of buildings and infrastructure. Because dune crest elevations within each monitored area matched the zonal averages, the researchers could be confident their measurements captured the character of each geomorphic state rather than local anomalies.</p>
<p>During the storm period, the pattern was stark. Every monitored area lost sediment from dunes, beach, and inner shoreface, while deposition accumulated in the back-barrier and on the outer shoreface. The numbers upended a common assumption: 92 percent of all storm-period deposition landed on the outer shoreface, seaward of the island, while only 8 percent reached the back-barrier as classic overwash. In other words, Sandy was far more efficient at pushing sand offshore than onshore. Only 19 percent of the sand stripped from the dunes could be accounted for in washover deposits. Overall, deposition exceeded measured erosion by about six percent, suggesting some sediment arrived from outside the study boundaries, but the dominant story was a massive seaward export of the island&#8217;s own material.</p>
<p>The alongshore variability was equally striking. In the transgressive Zone 1, where dunes are low and discontinuous, washover accounted for 92 percent of dune losses, exactly the behavior long assumed for overwash-dominated barriers. But in the other zones, washover fractions collapsed to as little as one percent of total deposited volume. Fluxes to the outer shoreface were, on average, 5.5 times the magnitude of overwash fluxes, ranging from 2.4 times in the transgressive zone to a remarkable 99 times in the geologically progradational Zone 3. Even when storm conditions were optimized to drive overwash, the seaward sink dominated. The practical consequence is stark: measurements of overwash from transgressive barriers should be treated as maxima, and models calibrated on them may substantially overestimate how much sand storms deliver to island interiors, the very process that builds elevation and buys time against rising seas.</p>
<p>The post-storm period told a different and more troubling story. Across all monitored areas, sediment accumulated everywhere except the outer shoreface, yet total post-storm deposition represented only 33 percent of the volume that had been eroded from the outer shoreface during the storm. After nearly five years, 18 percent of the storm&#8217;s outer shoreface deposit remained in place, and the researchers concluded that almost half of the storm deposit had been transported beyond their analysis boundaries, either alongshore or into deeper water, rather than returning to rebuild the island. Post-storm fluxes averaged ten times smaller than storm fluxes, and at those rates, full dune recovery would take nearly 15 years on average, with the slowest zone requiring more than 19 years. Beach recovery times ranged from one year near the island&#8217;s western littoral endpoint to 12.5 years in the transgressive zone.</p>
<p>Nature did not act alone. Hurricane Sandy opened several breaches, and one, Wilderness Inlet, was left to evolve naturally, while engineers placed an estimated six million cubic meters of nourishment sand elsewhere on the island. The inlet reshaped the sediment budget in dramatic ways. Updrift of the breach, the growing ebb tidal delta trapped sand and every environment accumulated. Downdrift, the inlet starved the historically progradational Zone 2 of supply, producing post-storm losses eleven times greater than measured accumulation and post-storm erosion that exceeded storm-period deposition by about ten percent. The team estimated that roughly 40 percent of the sediment lost downdrift of the inlet fed a growing flood tidal delta, and that inlet-related landward transport contributed about 67 percent of the post-storm landward sediment transfer, twice the net washover volume measured in adjacent environments. Suppressing such breaches, the authors suggest, may inadvertently strip barriers of a powerful landward sediment pathway.</p>
<p>Tallying the full five-year record, the outcome was sobering. Despite human intervention, the monitored areas suffered a net loss of roughly 1.2 million cubic meters of sediment, split about 62 percent terrestrial and 38 percent shoreface. Overall recovery reached only 16 percent of what the storm removed from beach, dune, and inner shoreface environments, distributed as 13 percent dune recovery, 39 percent beach recovery, and 11 percent inner shoreface recovery. Recovery patterns tracked geomorphology: the nourished, elongational western zone recovered 161 percent of its storm losses, while the transgressive eastern zone recovered barely half, with much of its gain buried on the inner shoreface rather than rebuilding dunes or beaches. The researchers note that if the inlet-impacted zone were excluded, recovery would have exceeded 80 percent, underscoring the short-term geomorphic cost that inlets extract even as they may build long-term resilience.</p>
<p>The study also forged a direct link between the island&#8217;s hidden geology and its storm behavior. Previous work had shown that shoreface sediment volume increases from east to west along Fire Island, and the new flux measurements mirror that gradient: the elongational western zone exhibited the highest shoreface fluxes, while zones with thinner shoreface reservoirs showed elevated beach erosion instead. Localized deficits in the shoreface, the authors argue, force the terrestrial part of the island to bear more of the storm&#8217;s burden. This connection between shoreface sediment availability and storm-time fluxes extends decades of geological insight into the compressed timescales of individual storms and may help explain why shoreline erosion trends correlate with thin shoreface deposits.</p>
<p>For coastal managers facing rising seas and a dwindling global sand supply, the message is double-edged. On one hand, the research shows that recovery from extreme storms is far slower and less complete than typical monitoring campaigns assume, and that shoreface storm deposits do not reliably march back onshore as some models of coastal adaptation presume. Simplified models that treat the shoreface as a linear, instantly responsive buffer may overestimate recovery rates and underestimate barrier vulnerability. On the other hand, the work offers a strategic lever: because different geomorphic states respond so differently to the same sediment inputs, managers could tailor nourishment placement to island geometry, maximizing near-term protection where recovery is naturally efficient while preserving the overwash and inlet pathways that sustain barriers over centuries. The alternative, holding every barrier in place with ever-larger artificial dunes, risks severing the very sediment circuits that allow these islands to keep pace with the ocean. As storm intensity and sea level continue to climb, the five-year ledger from Fire Island suggests that the geometry of a barrier island is not a detail of its response to climate change. It is the response.</p>
<p><strong>Subject of Research:</strong> Storm-driven and post-storm sediment fluxes on the geomorphically complex barrier island Fire Island, New York</p>
<p><strong>Article Title:</strong> Barrier island geomorphic complexity drives storm and post-storm response</p>
<p><strong>Article References:</strong> Miselis, J. L., Buster, N. A., Ciarletta, D. J., Bernier, J. C., Wei, E. A., &amp; Palermo, R. V. (2026). Barrier island geomorphic complexity drives storm and post-storm response. <em>Nature Communications, 17</em>(1), Article 10172. <a href="https://doi.org/10.1038/s41467-026-77143-6" rel="noopener noreferrer">https://doi.org/10.1038/s41467-026-77143-6</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.1038/s41467-026-77143-6" rel="noopener noreferrer">10.1038/s41467-026-77143-6</a></p>
<p><strong>Keywords:</strong> barrier islands, Hurricane Sandy, sediment flux, shoreface, overwash, coastal geomorphology, sea-level rise, Fire Island, tidal inlets, beach nourishment, post-storm recovery, Nature Communications</p>
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		<post-id xmlns="com-wordpress:feed-additions:1">262610</post-id>	</item>
		<item>
		<title>Salinity Swings in Asia&#8217;s Largest Lagoon Are Reshaping Fish and Fisher Livelihoods</title>
		<link>https://scienmag.com/salinity-swings-in-asias-largest-lagoon-are-reshaping-fish-and-fisher-livelihoods/</link>
		
		<dc:creator><![CDATA[Violet Maxwell]]></dc:creator>
		<pubDate>Fri, 02 Oct 2026 16:12:28 +0000</pubDate>
				<category><![CDATA[Earth Science]]></category>
		<category><![CDATA[artisanal fisheries]]></category>
		<category><![CDATA[artisanal fisheries in India]]></category>
		<category><![CDATA[biodiversity]]></category>
		<category><![CDATA[brackish water]]></category>
		<category><![CDATA[Chilika Lagoon]]></category>
		<category><![CDATA[climate change]]></category>
		<category><![CDATA[climate change and salinity swings in coastal lagoons]]></category>
		<category><![CDATA[cyclones]]></category>
		<category><![CDATA[ecological significance of wetlands in Odisha]]></category>
		<category><![CDATA[effects of salinity on food webs in brackish waters]]></category>
		<category><![CDATA[environmental management of Chilika Lagoon]]></category>
		<category><![CDATA[fishery sector growth in India]]></category>
		<category><![CDATA[global importance of small-scale fisheries]]></category>
		<category><![CDATA[habitat degradation]]></category>
		<category><![CDATA[hydrology]]></category>
		<category><![CDATA[impact on fish communities and fisher livelihoods]]></category>
		<category><![CDATA[Odisha]]></category>
		<category><![CDATA[open-access research on lagoon ecology]]></category>
		<category><![CDATA[resilience of coastal ecosystems to salinity changes]]></category>
		<category><![CDATA[salinity]]></category>
		<category><![CDATA[Salinity fluctuations in Chilika Lagoon]]></category>
		<category><![CDATA[small-scale fisheries]]></category>
		<category><![CDATA[socio-economic impact on coastal households]]></category>
		<category><![CDATA[tidal inlets]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=228503</guid>

					<description><![CDATA[A new review shows that fluctuating salinity in India's Chilika Lagoon drives fish biodiversity, habitat health, and the livelihoods of more than 400,000 artisanal fishers.]]></description>
										<content:encoded><![CDATA[<p>Chilika Lagoon, the vast brackish water body that stretches along India&#8217;s eastern coast in the state of Odisha, has long been celebrated as one of the world&#8217;s most ecologically significant wetlands. A new open-access review published in Discover Oceans argues that the lagoon&#8217;s fate, and the fate of the hundreds of thousands of artisanal fishers who depend on it, hinges on a single master variable: salinity. The review, led by Avisweta Nandy of Sri Sri University with Dwity Sundar Rout and Pritam Tripathy of Centurion University, synthesizes decades of research to show how shifting salt concentrations ripple through the lagoon&#8217;s food webs, fish communities, and ultimately the household economies of coastal villages.</p>
<p>The scale of the human stakes is enormous. India is the world&#8217;s second-largest fish producer, with a record 175.45 lakh tonnes of fish production in 2023, and its fisheries sector has grown by 10.87 percent since 2014–15. Odisha alone produces roughly 8.73 lakh metric tonnes annually, drawing on a 480 kilometre coastline and nearly 11 lakh hectares of inland and brackish waters. Globally, small-scale fisheries account for more than 90 percent of active fishers and support nearly two-thirds of the global fish catch, yet they remain chronically underreported in statistics and overlooked in policy. Chilika exemplifies this blind spot: more than 400,000 fishers live in nearly 150 settlements around the lagoon, many operating under a unique governance system that grants exclusive fishing rights administered through cooperatives and supported by the Chilika Development Authority.</p>
<p>Salinity in Chilika is governed by a delicate tug-of-war between seawater pushing in through tidal inlets from the Bay of Bengal and freshwater discharging from inland rivers. The lagoon spans nearly 1,100 square kilometres during the monsoon and contracts to about 906 square kilometres in the dry months, with an average depth of just 1.8 metres. This shallow, hydrologically dynamic system is divided into four ecological sectors: the freshwater-dominated Northern Sector, the Central and Southern Sectors, and the saline-rich Outer Channel. Seasonal salinity ranges from nearly zero during the rains to around 17 parts per thousand in winter and roughly 35 parts per thousand in summer, creating one of the steepest estuarine gradients in Asia and a natural laboratory for studying how salt shapes biodiversity.</p>
<p>The historical record reveals dramatic swings. Average salinity fell from 22.3 parts per thousand in 1957–1958 to between 9.4 and 11.8 parts per thousand by the early 1960s, and dropped to a critical low of 8.3 parts per thousand by 1999. The culprit was partly geomorphological: the commissioning of the Hirakud Dam on the Mahanadi River in 1957 unexpectedly increased the silt load entering the lagoon, driving progressive sedimentation, choking of the Arakhakuda mouth, reduced tidal exchange, salinity decline, and rampant weed overgrowth. In response, an artificial sea mouth was opened near Sipakuda village on 23 September 2000, restoring seawater ingress. Natural inlets subsequently formed at Gabakunda in 2008, Dhalabali in 2012, and during Cyclone Phailin in October 2013, and research by Panda and Mohanty showed that the shift from a single to a multiple inlet system between 2006 and 2009 produced pronounced changes in annual mean salinity, with cascading effects on sedimentation, marine species intrusion, and ecological balance.</p>
<p>Extreme weather adds another layer of volatility. The Super Cyclone of 1999 devastated fisheries resources and infrastructure. Cyclone Phailin in 2013 triggered a dramatic post-monsoon salinity decline and altered nutrient concentrations, lowering phosphate and nitrate while raising silicate and ammonia. Cyclone Fani in 2019, striking in May during the lagoon&#8217;s peak salinity period, instead elevated salinity relative to other storms, while Hudhud in 2014 had minimal impact. Data from 1999 to 2021 show average salinity of 10.69 parts per thousand, ranging from 0.1 to 36.9, with the Northern Sector experiencing sharp fluctuations and the Southern Sector remaining more stable. Most recently, a deep depression over the northwestern Bay of Bengal on 13 July 2022 opened a new inlet, driving Outer Channel salinity from 21 to 34 parts per thousand in June down to zero to 2 parts per thousand by August. Broader climate phenomena, including the El Niño–Southern Oscillation, modulate these patterns by influencing precipitation, river discharge, and lagoon–sea exchange.</p>
<p>The biological consequences are striking. Fish diversity in Chilika is structured along the salinity gradient: freshwater species dominate the north, brackish species the centre and south, and the tidal Outer Channel supports both brackish and marine fishes. Species counts have climbed from 138 aquatic species recorded in 1918 to 336 by 2008, including 261 finfish, 28 prawns, and 34 crabs, before slipping slightly to 317 in 2023 across 207 genera, 88 families, and 23 orders. The lagoon also shelters around 700 plant and 800 animal species, including the endangered Irrawaddy dolphin, and serves as a critical stopover on the Central Asian Flyway for migratory birds. Salinity shifts impose oxidative stress on aquatic organisms, altering survival, reproduction, and distribution, and declining salinity has stressed brackish biota such as prawns, which form the backbone of the local fishery.</p>
<p>The 2000 hydrological intervention, however, demonstrates that salinity management can also drive recovery. Enhanced seawater exchange improved recruitment of juvenile marine fish, lifting fish landings from 11,989 metric tonnes in 2001–02 to 14,228 metric tonnes in 2011–12, documenting 56 new species, and coinciding with the reappearance of the Irrawaddy dolphin. Phytoplankton communities responded too: diatoms replaced cyanobacteria and came to dominate up to 72 percent of phytoplankton biomass, benefiting fish production. After the new inlet opened in July 2022, landings rose to 223.62 metric tonnes, with mullets and other marine species featuring prominently. Yet fishers also reported disturbances, including sand infestation, fluctuating water depths, and the arrival of unfamiliar marine organisms such as stingrays, octopuses, and jellyfish, which reshaped fishing seasons and species composition.</p>
<p>Habitat degradation compounds the problem. Declining salinity converts brackish habitats into freshwater-dominated systems, eliminating niches for estuarine species such as mullets and anchovies, narrowing tidal channels, and degrading seagrass meadows that serve as critical spawning and feeding grounds for prawns and crabs. Long-term desalination has fuelled invasive weed growth, particularly in the northern sector, while excessive sedimentation and intensive prawn aquaculture, locally known as gheri or bund fishing, have altered hydrology and sediment transport, impeding fish migration and nutrient flow. Embankments and dams further disrupt natural flow, fragmenting habitats and reducing species resilience. The socioeconomic fallout is cascading: declining catches and unstable incomes exacerbate poverty, malnutrition, and occupational migration, and in some cases entire villages have shifted away from fishing altogether, while shrimp aquaculture introduced in the 1980s disrupted traditional access rights and intensified competition.</p>
<p>The review&#8217;s authors frame salinity not merely as a physical parameter but as a socio-ecological determinant linking ecological balance with human well-being, and they chart a path forward. Key strategies include restoring ecological buffers such as mangroves, seagrass beds, and wetlands that stabilize salinity and provide fish nurseries; promoting livelihood diversification through eco-tourism, aquaculture, and small enterprises; enforcing fisheries laws such as the Marine Fishing Regulation Acts in collaboration with local communities; and building fisher capacity in adaptive practices like seasonal restrictions, spatial management, and catch diversification. Regular monitoring of salinity and hydrological parameters is deemed indispensable for guiding adaptive management, and economic valuation shows fishery resources account for over 71 percent of the lagoon&#8217;s total economic value, underscoring what is at stake.</p>
<p>Ultimately, the study lays the groundwork for future econometric analyses quantifying how salinity variation cascades through biodiversity and artisanal livelihoods. As climate change accelerates sea-level rise, saltwater intrusion, and cyclone intensity across low-lying Asian coasts, Chilika&#8217;s experience offers a cautionary tale and a template: salinity management, if pursued inclusively and grounded in fishers&#8217; rights, can allow Asia&#8217;s largest brackish water lagoon to thrive both as an ecological jewel and as a lifeline for the communities whose fortunes rise and fall with its salt.</p>
<p><strong>Subject of Research:</strong> Salinity dynamics and their ecological and socioeconomic impacts on artisanal fisheries in Chilika Lagoon, India</p>
<p><strong>Article Title:</strong> Salinity changes and their environmental impacts on artisanal fisheries in Chilika Lagoon</p>
<p><strong>Article References:</strong> Salinity changes and their environmental impacts on artisanal fisheries in Chilika Lagoon. (n.d.). <a href="https://doi.org/10.1007/s44289-026-00137-1" rel="noopener noreferrer">https://doi.org/10.1007/s44289-026-00137-1</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.1007/s44289-026-00137-1" rel="noopener noreferrer">10.1007/s44289-026-00137-1</a></p>
<p><strong>Keywords:</strong> Chilika Lagoon, salinity, artisanal fisheries, brackish water, climate change, biodiversity, tidal inlets, cyclones, Odisha, small-scale fisheries, habitat degradation, hydrology</p>
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