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	<title>eelgrass &#8211; Science</title>
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	<title>eelgrass &#8211; Science</title>
	<link>https://scienmag.com</link>
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		<title>More Seeds Yield More Shoots, but Not Higher Per-Seed Establishment in a Clam-Mediated Seagrass Restoration Experiment</title>
		<link>https://scienmag.com/more-seeds-yield-more-shoots-but-not-higher-per-seed-establishment-in-a-clam-mediated-seagrass-restoration-experiment/</link>
		
		<dc:creator><![CDATA[Alan Morgan]]></dc:creator>
		<pubDate>Fri, 16 Oct 2026 13:08:20 +0000</pubDate>
				<category><![CDATA[Earth Science]]></category>
		<category><![CDATA[Science News]]></category>
		<category><![CDATA[bivalve facilitation]]></category>
		<category><![CDATA[bivalve-assisted seagrass planting]]></category>
		<category><![CDATA[challenges of seagrass re-establishment]]></category>
		<category><![CDATA[clam-mediated seed delivery]]></category>
		<category><![CDATA[coastal ecosystems]]></category>
		<category><![CDATA[ecomimicry]]></category>
		<category><![CDATA[eelgrass]]></category>
		<category><![CDATA[eelgrass (Zostera marina) restoration]]></category>
		<category><![CDATA[field experiment in North Carolina]]></category>
		<category><![CDATA[hard clams]]></category>
		<category><![CDATA[impact of seed quantity on establishment success]]></category>
		<category><![CDATA[large-scale habitat restoration methods]]></category>
		<category><![CDATA[marine conservation]]></category>
		<category><![CDATA[marine conservation strategies]]></category>
		<category><![CDATA[marine ecosystem restoration]]></category>
		<category><![CDATA[Mercenaria mercenaria]]></category>
		<category><![CDATA[North Carolina]]></category>
		<category><![CDATA[Seagrass restoration]]></category>
		<category><![CDATA[seed attachment techniques]]></category>
		<category><![CDATA[seed density]]></category>
		<category><![CDATA[seed dispersal and burial]]></category>
		<category><![CDATA[seed-based restoration]]></category>
		<category><![CDATA[seed-based seagrass planting]]></category>
		<category><![CDATA[Zostera marina]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=285190</guid>

					<description><![CDATA[Seagrass meadows rank among the most valuable ecosystems on the planet, buffering shorelines, storing carbon, and sheltering juvenile fish, yet they continue to vanish at alarming rates worldwide. Restoring them at scale has long been a logistical nightmare, and seed-based]]></description>
										<content:encoded><![CDATA[<p>Seagrass meadows rank among the most valuable ecosystems on the planet, buffering shorelines, storing carbon, and sheltering juvenile fish, yet they continue to vanish at alarming rates worldwide. Restoring them at scale has long been a logistical nightmare, and seed-based approaches—while promising because they can cover far larger areas than transplanting shoots without damaging donor meadows—suffer from notoriously low and variable establishment rates. Now, a field experiment off the coast of North Carolina has put one of the most creative seed-delivery ideas in marine restoration to the test: glue eelgrass seeds onto live clams and let the bivalves do the burying. The verdict, published in Frontiers in Marine Science, is both encouraging and instructive: the clam technique works, but how many seeds you attach matters far more than how you deploy them.</p>
<p>The study, led by Cori Lopazanski and colleagues at the Duke University Marine Lab, focused on eelgrass (Zostera marina), a temperate seagrass whose reproductive shoots were collected from beds in Back Sound in May 2025. Mature seeds were naturally released in indoor flow-through tanks at the Duke facility in early July, harvested from the tank bottoms, and stored in fine nylon mesh bags until deployment that October. Before planting, the team randomly tested 100 seeds for viability using tetrazolium staining and found 89 percent viable—a solid starting point for any restoration effort.</p>
<p>The delivery mechanism is where the experiment gets genuinely novel. Juvenile hard clams (Mercenaria mercenaria), roughly two centimeters long and sourced from an aquaculture program at Carteret Community College, served as living seed taxis. A gelatin-based adhesive—dissolved in saltwater at 9 percent weight per volume, heated to 35 degrees Celsius, then cooled to 25 before application—was pipetted onto one shell of each clam. Seeds were arranged in a single layer and sealed under a second thin coat. The clams were refrigerated at 9 degrees for 30 minutes to set the adhesive, transported in coolers, and deployed the same day, with total handling time under four hours. Preliminary lab trials showed the adhesive dissolved and seeds detached within 8 to 12 hours in 22-degree saltwater—roughly the ambient October temperature in Back Sound—while clams placed in tanks with sediment typically buried themselves fully within 75 minutes, reaching a mean depth of about three centimeters.</p>
<p>The experimental design crossed ten seed densities (10 to 100 seeds per clam in increments of 10) with two placement treatments—manually buried to two centimeters or simply placed on the sediment surface—in a fully factorial layout with four replicates per combination, totaling 80 plots of 0.25 by 0.25 meters arranged in a gridded configuration. The site, a sheltered shallow subtidal sandy area near Harker&#8217;s Island separated from adjacent salt marsh, oyster reef, and seagrass habitat by at least 10 meters, was monitored biweekly from November 2025 through April 2026, with researchers counting live shoots and measuring the heights of up to five randomly selected shoots per plot each visit.</p>
<p>The results tell a clear quantitative story. Shoot establishment rose significantly with seed density: each additional 10 seeds planted increased the expected number of established shoots by 24.2 percent (95 percent CI: 6.6 to 44.6 percent). Model predictions indicated that going from 10 to 100 seeds per clam raised expected shoot counts from 1.4 to 9.8 per plot. Shoots appeared from December onward, and higher densities showed progressively greater shoot abundance through time, supported by a temporal hurdle analysis showing the probability of observing at least one live shoot increased more strongly at higher densities. But here is the crucial nuance: the proportion of seeds that actually produced shoots did not vary with density. Per-seed establishment hovered between roughly 5 and 12 percent across all planting rates, with no statistically significant differences—meaning more seeds yielded more shoots, but did not improve the odds for any individual seed.</p>
<p>Clam placement, meanwhile, turned out to be nearly irrelevant to the restoration outcome. Manually buried clams were more likely to be detected during the first two post-deployment surveys, and shell fragments were more common in surface treatments (62.5 percent of surface plots versus 40 percent of buried plots), hinting at greater predation or mortality among surface-deployed clams. Yet confirmed clam presence showed no association with final shoot density, per-seed establishment, or final shoot height. Shoot growth trajectories were broadly comparable between placement treatments, though shoots in higher-density treatments became consistently taller during the latter half of the experiment—possibly an early sign of positive interactions among neighbors, or of competition for light as local canopy density increased.</p>
<p>The low clam persistence in both treatments is striking. Juvenile clams are vulnerable to blue crabs, mud crabs, gastropods, and rays, and the team suggests predation is a plausible explanation for the losses. But the key insight is that seed incorporation likely occurred rapidly regardless of clam fate: because the gelatin adhesive released seeds within 8 to 12 hours, seeds probably detached soon after deployment—potentially after clams had burrowed, carrying them below the sediment surface where conditions favor germination. This timing, the authors argue, is likely the critical design variable for the technique, with the goal of synchronizing seed release with initial sediment incorporation rather than maintaining long-term attachment. Further optimization could examine different adhesive formulations across temperatures, salinities, sediment types, and hydrodynamic conditions, and predator-exclusion treatments could distinguish direct seed consumption from displacement during clam predation.</p>
<p>Importantly, the authors caution that the limited relationship between clam persistence and restoration outcomes should not be read as evidence that bivalves do not facilitate seagrass. Previous work has shown persistent bivalve populations can enhance seagrass biomass, growth, patch expansion, and disturbance resilience through mechanisms including reduced herbivory, enhanced nutrient availability, and improved water clarity. But this experiment tracked only the first six months post-deployment and used a single juvenile clam per plot—a density and timescale likely insufficient to generate the ecosystem-engineering effects associated with mature bivalve populations. The absence of density dependence in per-seed establishment also suggests that neither competition nor facilitation strongly shaped seedling establishment during the first growing season; instead, establishment appears governed by seed viability and local environmental conditions.</p>
<p>From a practical standpoint, the findings reframe the central question of seed-based restoration. Because per-seed establishment remained constant across a tenfold range of densities, practitioners can select seed density per clam based on the desired restoration configuration rather than per-seed performance. Concentrating many seeds on fewer clams should produce dense patches; spreading the same number of seeds across more clams should yield a similar total number of shoots distributed over a larger area. And because manually burying clams offered little measurable benefit over surface placement, the less labor-intensive surface deployment may be sufficient for large-scale efforts—a meaningful efficiency gain when seed availability frequently constrains restoration scale.</p>
<p>The study also carries a caveat about its design: seed densities were assigned by row rather than fully randomized, limiting the ability to separate density effects from unmeasured spatial variation, though the experiment occupied a small, visually uniform 5.5 by 7 meter area where strong gradients were unlikely. Whether these results hold in higher-energy environments, at larger scales, or over longer timescales—when density-dependent facilitation or competition may emerge as patches develop—remains an open question. Still, the work positions clam-mediated seed deployment as a practical addition to the growing suite of seed-based restoration tools and illustrates a broader principle the authors call ecosystem technology, or ecotech: harnessing natural organismal behaviors to design restoration techniques that work with, rather than against, ecological processes. As seagrass losses accelerate globally, approaches that let clams do the digging may prove exactly the kind of scalable innovation coastal restoration has been waiting for.</p>
<p><strong>Subject of Research:</strong> Clam-mediated seed deployment for eelgrass seagrass restoration</p>
<p><strong>Article Title:</strong> More seeds yield more shoots, but not higher per-seed establishment in a clam-mediated seagrass restoration experiment</p>
<p><strong>Article References:</strong> Lopazanski, C., Cutshaw, C. L., Ibrahim, M., Morton, J. P., &amp; Silliman, B. R. (2026). More seeds yield more shoots, but not higher per-seed establishment in a clam-mediated seagrass restoration experiment. <em>Frontiers in Marine Science, 13</em>, Article 1972882. <a href="https://doi.org/10.3389/fmars.2026.1972882" rel="noopener noreferrer">https://doi.org/10.3389/fmars.2026.1972882</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.3389/fmars.2026.1972882" rel="noopener noreferrer">10.3389/fmars.2026.1972882</a></p>
<p><strong>Keywords:</strong> seagrass restoration, eelgrass, Zostera marina, seed density, hard clams, Mercenaria mercenaria, bivalve facilitation, seed-based restoration, marine conservation, North Carolina, ecomimicry, coastal ecosystems</p>
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		<post-id xmlns="com-wordpress:feed-additions:1">285190</post-id>	</item>
		<item>
		<title>Underwater Grasses in Chesapeake Bay Rise 7 Percent as Salty Waters Lead Recovery</title>
		<link>https://scienmag.com/underwater-grasses-in-chesapeake-bay-rise-7-percent-as-salty-waters-lead-recovery/</link>
		
		<dc:creator><![CDATA[Violet Maxwell]]></dc:creator>
		<pubDate>Sat, 12 Sep 2026 23:34:09 +0000</pubDate>
				<category><![CDATA[Marine]]></category>
		<category><![CDATA[aerial survey of Chesapeake Bay submerged plants]]></category>
		<category><![CDATA[Chesapeake Bay]]></category>
		<category><![CDATA[Chesapeake Bay underwater grass recovery]]></category>
		<category><![CDATA[Chesapeake Bay Watershed restoration goals]]></category>
		<category><![CDATA[coastal and marine sciences research on estuary ecosystems]]></category>
		<category><![CDATA[ecological significance of underwater grass meadows]]></category>
		<category><![CDATA[eelgrass]]></category>
		<category><![CDATA[effects of nutrient pollution on aquatic habitats]]></category>
		<category><![CDATA[environmental restoration progress in Chesapeake Bay]]></category>
		<category><![CDATA[estuary health]]></category>
		<category><![CDATA[habitat restoration]]></category>
		<category><![CDATA[historical decline and rebound of underwater grasses]]></category>
		<category><![CDATA[impact of salty waters on estuary ecosystems]]></category>
		<category><![CDATA[influence of salinity changes on aquatic plant growth]]></category>
		<category><![CDATA[long-term trends in Chesapeake Bay habitat health]]></category>
		<category><![CDATA[nutrient reduction]]></category>
		<category><![CDATA[Polyhaline Zone]]></category>
		<category><![CDATA[Seagrass restoration]]></category>
		<category><![CDATA[submerged aquatic vegetation]]></category>
		<category><![CDATA[submerged aquatic vegetation increase]]></category>
		<category><![CDATA[VIMS]]></category>
		<category><![CDATA[water clarity]]></category>
		<category><![CDATA[water quality]]></category>
		<category><![CDATA[widgeon grass]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=199708</guid>

					<description><![CDATA[An annual aerial survey found Chesapeake Bay underwater grasses grew 7 percent in 2025 to 89,385 acres, the highest coverage since 2018, driven largely by expanding eelgrass and widgeon grass in the estuary's saltier waters.]]></description>
										<content:encoded><![CDATA[<p>The Chesapeake Bay&#8217;s underwater grass meadows, long regarded as one of the most sensitive barometers of the estuary&#8217;s ecological condition, expanded by 7 percent in 2025, according to researchers at William &amp; Mary&#8217;s VIMS &amp; Batten School of Coastal &amp; Marine Sciences. The annual Bay-wide aerial survey documented a total of 89,385 acres of submerged aquatic vegetation across the Chesapeake Bay and its tidal tributaries, an increase of 6,134 acres over the 2024 estimate. The figure marks the highest Bay-wide acreage recorded since 2018 and brings the estuary within striking distance of the Chesapeake Bay Watershed Agreement&#8217;s 2030 interim restoration goal of 90,000 acres. It also represents roughly 45 percent of the long-term restoration target of 196,600 acres, a benchmark rooted in historical reconstructions of how much grass the Bay once supported.</p>
<p>The new numbers capture both how far the ecosystem has come and how much work remains. When systematic monitoring began in 1984, underwater grass coverage had collapsed to approximately 39,000 acres, the residue of decades of nutrient pollution, sediment runoff and habitat degradation that pushed the Bay&#8217;s once-extensive meadows to historic lows in the 1980s. Abundance has since more than doubled, a trajectory researchers attribute in large part to nutrient reduction measures implemented throughout the 64,000-square-mile watershed. The 2025 results suggest those sustained investments continue to pay ecological dividends, even as climate change, shifting land-use pressures and localized environmental stressors introduce new complications for restoration planners.</p>
<p>Christopher J. Patrick, associate professor and director of the SAV Program at VIMS &amp; the Batten School, said the survey reflects a recovery that is both encouraging and uneven. This year&#8217;s results, he noted, demonstrate that the Bay is moving in the right direction while also revealing considerable complexity in the composition and behavior of its underwater grass communities. Strong recovery continues in the main basin, particularly in the saltier portions of the Bay, while some localized freshwater areas have experienced setbacks. Patrick emphasized that the mainstem recoveries are especially meaningful because they indicate that watershed-level management actions are producing measurable positive outcomes at the scale of the entire estuary.</p>
<p>Much of the 2025 increase was driven by continued expansion in the Bay&#8217;s higher-salinity waters. The Polyhaline Zone, which encompasses the saltiest waters near the Bay&#8217;s mouth, grew from 25,266 acres in 2024 to an estimated 28,142 acres in 2025, setting a new record for the second consecutive year. The moderately salty Mesohaline Zone expanded nearly 15 percent, from 33,033 acres in 2024 to an estimated 37,879 acres in 2025. Researchers attribute much of this growth, including the record-setting expansion of eelgrass meadows, to sustained year-over-year improvements in water clarity in the lower Bay. Recent work has documented consistent water-quality gains throughout the Chesapeake Bay mainstem over the past several years, and the concurrent expansion of eelgrass, both in the size of existing beds and into deeper waters, is consistent with those improvements.</p>
<p>Similar processes appear to be driving the expansion of widgeon grass in the middle portion of the Bay, a species that is still rebounding from a dramatic crash triggered by exceptionally wet conditions in 2018. Heavy rainfall years deliver pulses of nutrients and sediment that cloud the water and suppress the light these plants need for photosynthesis, and the 2018 event demonstrated how vulnerable even recovering beds can be to climatic variability. The fact that widgeon grass has reestablished itself in the years since underscores the resilience of these communities when the underlying conditions that govern light availability begin to stabilize. Patrick described the pace of change in the lower Bay as remarkable, noting how rapidly seagrass can recover when conditions are right and expressing hope that the Bay&#8217;s ultimate seagrass restoration goals remain achievable.</p>
<p>Despite the Bay-wide gains, the survey revealed distinct declines in other portions of the estuary, a reminder that aggregate statistics can mask divergent regional trajectories. The Tidal Fresh Zone, a collection of spatially isolated upstream rivers and embayments, experienced a small decline, falling from 20,221 acres to an estimated 18,653 acres. Researchers observed particularly significant losses in several Virginia tributaries, including portions of the upper Rappahannock River. These declines were driven largely by reductions in Hydrilla verticillata, an invasive aquatic plant commonly known as water thyme that has expanded and contracted across multiple river systems in recent years. Because hydrilla can dominate freshwater beds, its fluctuations can swing regional totals even when native vegetation remains comparatively stable.</p>
<p>The slightly salty Oligohaline Zone, by contrast, remained relatively stable overall at just over 4,700 acres, with gains in several portions of the Bay helping to offset losses elsewhere. Patrick stressed that the Bay is not a single ecosystem but a collection of many distinct habitats, each responding differently to rainfall, water quality, salinity and other environmental factors and stressors. What emerged from this year&#8217;s survey, he said, is a reminder that Bay-wide trends are really the sum of many regional stories. Researchers say these contrasting patterns highlight the complexity of restoring underwater grasses across a watershed that spans parts of six states and the District of Columbia, where geography, land use, rainfall patterns, water clarity and local environmental conditions all shape how grass beds respond from one year to the next.</p>
<p>The ecological stakes of this recovery extend well beyond the meadows themselves. Underwater grasses provide essential habitat for fish, blue crabs, waterfowl and countless other species, functioning as nursery grounds, foraging areas and refuge from predators. They also perform a suite of ecosystem services that directly improve water quality: absorbing excess nutrients, stabilizing sediments, reducing shoreline erosion, sequestering carbon and producing oxygen through photosynthesis. Because submerged aquatic vegetation responds quickly to changes in environmental conditions, scientists consider it one of the most sensitive and informative indicators of overall Bay health, a living gauge that integrates the effects of upstream land management, wastewater treatment, atmospheric deposition and climate variability into a single measurable signal.</p>
<p>Historical evidence suggests the Chesapeake Bay once supported between 200,000 and 600,000 acres of underwater grasses, a range that dwarfs today&#8217;s totals and frames the scale of the restoration challenge. The 2025 acreage of 89,385 acres, while the highest since 2018, still leaves the Bay at less than half of the 196,600-acre long-term goal. Yet the trajectory of the past four decades offers what researchers describe as genuine grounds for optimism. Recovery has proven possible, Patrick said, and the gains documented since monitoring began reflect the benefits of cleaner water and sustained restoration effort. Continuing that progress, he cautioned, will require ongoing support for science, habitat conservation and water-quality improvements throughout the watershed. For the scientists who fly the aerial surveys each year and the managers who translate the results into policy, the 2025 findings serve as both a validation of past investments and a measure of the distance still to be traveled in restoring one of the world&#8217;s largest and most closely studied estuaries.</p>
<p><strong>Subject of Research:</strong> Annual monitoring of submerged aquatic vegetation recovery in the Chesapeake Bay</p>
<p><strong>Article Title:</strong> Chesapeake Bay underwater grasses increase 7%, buoyed by gains in salty waters</p>
<p><strong>Article References:</strong> Chesapeake Bay underwater grasses increase 7%, buoyed by gains in salty waters. (n.d.). <a href="https://www.eurekalert.org/news-releases/1143046" rel="noopener noreferrer">Original publication</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> Not provided</p>
<p><strong>Keywords:</strong> Chesapeake Bay, submerged aquatic vegetation, eelgrass, widgeon grass, water quality, seagrass restoration, water clarity, VIMS, estuary health, nutrient reduction, Polyhaline Zone, habitat restoration</p>
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		<post-id xmlns="com-wordpress:feed-additions:1">199708</post-id>	</item>
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