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	<title>river pollution &#8211; Science</title>
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	<title>river pollution &#8211; Science</title>
	<link>https://scienmag.com</link>
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		<title>Rare Microbes Hold the Reins in Acid-Polluted Rivers, Study Reveals</title>
		<link>https://scienmag.com/rare-microbes-hold-the-reins-in-acid-polluted-rivers-study-reveals/</link>
		
		<dc:creator><![CDATA[Morgan Morrow]]></dc:creator>
		<pubDate>Sun, 04 Oct 2026 04:51:26 +0000</pubDate>
				<category><![CDATA[Climate]]></category>
		<category><![CDATA[acid mine drainage]]></category>
		<category><![CDATA[acid mine drainage microbial communities]]></category>
		<category><![CDATA[biogeography]]></category>
		<category><![CDATA[co-occurrence network]]></category>
		<category><![CDATA[community assembly]]></category>
		<category><![CDATA[ecological roles of rare microbes in contaminated waters]]></category>
		<category><![CDATA[ecological significance of rare microbial taxa]]></category>
		<category><![CDATA[environmental geochemistry of acid mine drainage]]></category>
		<category><![CDATA[environmental microbiology]]></category>
		<category><![CDATA[heavy metals]]></category>
		<category><![CDATA[impact of heavy metals on river microbiota]]></category>
		<category><![CDATA[microbial adaptation to acid and metal stress]]></category>
		<category><![CDATA[microbial community structure in acid-polluted rivers]]></category>
		<category><![CDATA[microbial diversity in extreme environments]]></category>
		<category><![CDATA[microbial ecology]]></category>
		<category><![CDATA[microbial ecology in hostile aquatic ecosystems]]></category>
		<category><![CDATA[microbial sampling and analysis in contaminated sediments]]></category>
		<category><![CDATA[microbial survival in acidic river environments]]></category>
		<category><![CDATA[prokaryotes]]></category>
		<category><![CDATA[rare biosphere]]></category>
		<category><![CDATA[river pollution]]></category>
		<category><![CDATA[role of rare biosphere in biogeochemical processes]]></category>
		<category><![CDATA[sediment microbiology]]></category>
		<category><![CDATA[stochastic processes]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=233598</guid>

					<description><![CDATA[A new study of an acid mine drainage-impacted river shows that rare prokaryotic taxa, though nearly invisible, occupy keystone positions in microbial networks while abundant communities follow deterministic environmental gradients in sediments but not in water.]]></description>
										<content:encoded><![CDATA[<p>When acid mine drainage bleeds into a river, it transforms the waterway into one of the most hostile environments on Earth. Extreme acidity, dissolved iron, sulfate and a cocktail of heavy metals would seem to leave little room for life, yet microbial communities not only survive in these poisoned waters but organize themselves into complex ecological systems. A new study published in Environmental Geochemistry and Health has now dissected how these communities are built, and the findings upend a long-standing assumption: the microbes that matter most may be the ones you can barely detect.</p>
<p>The research, led by Yuguang Wang, Longqi Xu and colleagues at Central South University in Changsha, China, examined a river system impacted by acid mine drainage, sampling both the flowing water and the underlying sediments along the contamination gradient. Rather than treating the microbial community as a single entity, the team split it into three compartments: the whole prokaryotic community, the abundant taxa that dominate biomass, and the rare taxa that linger at vanishingly low concentrations. This partitioning matters because ecologists have increasingly recognized that the rare biosphere, the enormous reservoir of low-abundance microorganisms, may behave according to entirely different rules than its abundant counterparts.</p>
<p>The first major finding concerns spatial structure. In sediment habitats, diversity and composition of the whole community and of abundant taxa changed significantly along the river, tracking the geochemical shifts imposed by the drainage. The relative abundances of Gammaproteobacteria and Betaproteobacteria, classes that often thrive in the most acidic, metal-rich zones near the pollution source, declined progressively downstream. In their place, Alphaproteobacteria and members of the phylum Acidobacteriota increased, suggesting a succession of acid-tolerant specialists as conditions gradually moderated. This directional turnover mirrors patterns documented in other acid mine drainage systems across southern China, where environmental heterogeneity and geographic isolation jointly sculpt microbial succession.</p>
<p>Water habitats told a strikingly different story. Unlike the sediments, the water column showed no significant spatial variation in community diversity or composition for the whole community or abundant taxa. Instead, the water was characterized by genera such as Acidovorax and Acidocella, acidophilic bacteria well adapted to the chemically uniform, continuously mixed conditions of the river channel. The contrast between sediment and water underscores a fundamental principle of microbial biogeography: habitat type can override pollution gradients in determining which ecological forces dominate. Sediments, with their layered chemistry, particle surfaces and pore waters, create microenvironments where deterministic filtering by environmental conditions leaves a clear spatial fingerprint. The well-mixed water column, by contrast, homogenizes conditions and appears to erase much of that spatial signal.</p>
<p>To understand how these communities came to be, the researchers turned to the conceptual machinery of community assembly theory. Ecologists distinguish between deterministic processes, in which environmental selection favors organisms with suitable traits, and stochastic processes, in which random dispersal, ecological drift and historical contingency shape which species end up where. Using null model analysis, which compares observed community turnover against what would be expected by chance, the team quantified the relative contributions of heterogeneous selection, homogeneous selection, dispersal limitation, dispersal and undominated processes.</p>
<p>The verdict was clear: stochasticity rules, especially for the rare biosphere. Dispersal limitation and undominated processes, a category capturing the combined effects of weak selection and weak dispersal, generally dominated community assembly, and this was most pronounced for rare taxa. The alpha diversity of rare taxa showed no significant correlation with spatial distance in either sediments or water, indicating that these low-abundance organisms are distributed in ways that defy simple geographic or environmental gradients. For the abundant taxa and the whole community in sediments, however, deterministic processes, both heterogeneous and homogeneous selection, still played a role that could not be ignored. In other words, the dominant players in the sediment are filtered by the harsh chemistry of acid mine drainage, while the rare players arrive and persist largely by chance.</p>
<p>Perhaps the most provocative result came from the co-occurrence network analysis. When the researchers mapped which taxa appear together across samples, constructing a network of potential ecological interactions, they found that rare taxa occupied important topological positions. These are the nodes that connect distant parts of the network, acting as potential keystone species whose removal could restructure the entire community. The finding resonates with a growing body of evidence that the rare biosphere punches far above its numerical weight. Studies in fertilized soils, acidic soils and other ecosystems have shown that rare microorganisms can be major drivers of ecosystem multifunctionality, and theoretical work has argued that the rare biosphere may serve as a dormant seed bank that resuscitates during pulses of ecosystem activity.</p>
<p>Why would rare taxa occupy such influential positions in a system as extreme as an acid mine drainage river? One possibility is that rarity itself is a strategy. Many rare organisms are specialists with narrow environmental tolerances, active only in fleeting favorable microenvironments. In a chemically heterogeneous system, these specialists may broker interactions between abundant generalists, facilitating the transfer of metabolites such as organic acids, iron species or sulfur intermediates across guild boundaries. Another possibility is that network edges involving rare taxa reflect shared responses to fine-scale environmental variation that abundant taxa, buffered by their sheer numbers, do not experience. Either way, the result challenges the practice of focusing monitoring and remediation assessments solely on dominant organisms.</p>
<p>The study also carries practical implications for managing mine-polluted rivers. Acid mine drainage is a global problem, contaminating thousands of kilometers of waterways with acidity, iron, aluminum, manganese and toxic metalloids. Natural attenuation, the gradual reduction of pollutant loads by intrinsic physical, chemical and biological processes, depends heavily on microbial activity, particularly sulfate-reducing bacteria and iron-cycling organisms that can immobilize metals as sulfides and oxides. If rare taxa hold key positions in the interaction networks that underpin these functions, then perturbations that further reduce rare diversity, such as episodic acid pulses or engineering interventions that disturb sediments, could have outsized and unpredictable consequences for the river&#8217;s capacity to heal itself.</p>
<p>The research also refines how scientists should read microbial communities as pollution indicators. Previous work on copper-contaminated river sediments suggested that abundant taxa are more sensitive bio-indicators than rare ones, and the present study partly supports that view: abundant taxa in sediments responded strongly and predictably to the spatial environmental gradient. But the new findings add nuance. Abundant taxa may tell you where the pollution is, while rare taxa may tell you how the ecosystem is wired. Effective ecological evaluation of acid mine drainage impact, the authors suggest, requires tracking both compartments and recognizing that they are assembled by different forces.</p>
<p>Methodologically, the study exemplifies the current toolkit of microbial ecology. High-throughput amplicon sequencing of the 16S ribosomal RNA gene, processed through rigorous quality control and denoising pipelines, provided the taxonomic inventory. Environmental variables measured alongside the biological samples allowed the team to link community patterns to geochemistry. Null models converted patterns into process, and network analysis converted co-occurrence into hypotheses about interaction. This integrated approach is rapidly becoming the standard for disentangling the ecology of complex microbial systems, from Antarctic lakes to tropical ocean waters to contaminated rivers.</p>
<p>The broader message is one of humility about where ecological power resides. In a river poisoned by acid mine drainage, the visible story, the dominant Gammaproteobacteria near the source, the Acidobacteriota downstream, the Acidovorax in the water, is written by environmental selection and reads clearly along the pollution gradient. But the hidden story, the one told by dispersal limitation, random drift and the quiet influence of organisms too scarce to notice, may be just as important. As the rare biosphere continues to reveal itself across ecosystems, ecologists are learning that in microbial worlds, less may indeed be more, and the smallest players may hold the strings of the entire system.</p>
<p><strong>Subject of Research:</strong> Microbial community assembly of abundant and rare prokaryotic taxa in an acid mine drainage-impacted river system</p>
<p><strong>Article Title:</strong> Distinct ecological patterns of abundant and rare prokaryotic taxa across sediment and water habitats in an acid mine drainage-impacted river system</p>
<p><strong>Article References:</strong> Wang, Y., Xu, L., Ai, C., Chen, Z., Zhou, H., &amp; Cheng, H. (2026). Distinct ecological patterns of abundant and rare prokaryotic taxa across sediment and water habitats in an acid mine drainage-impacted river system. <em>Environmental Geochemistry and Health, 48</em>(15), Article 619. <a href="https://doi.org/10.1007/s10653-026-03523-y" rel="noopener noreferrer">https://doi.org/10.1007/s10653-026-03523-y</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.1007/s10653-026-03523-y" rel="noopener noreferrer">10.1007/s10653-026-03523-y</a></p>
<p><strong>Keywords:</strong> acid mine drainage, rare biosphere, microbial ecology, community assembly, co-occurrence network, prokaryotes, sediment microbiology, river pollution, heavy metals, stochastic processes, biogeography, environmental microbiology</p>
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		<post-id xmlns="com-wordpress:feed-additions:1">233598</post-id>	</item>
		<item>
		<title>Bubble Barriers Catch Floating Microplastics but Let Smaller Particles Slip Through</title>
		<link>https://scienmag.com/bubble-barriers-catch-floating-microplastics-but-let-smaller-particles-slip-through/</link>
		
		<dc:creator><![CDATA[Denise Maddox]]></dc:creator>
		<pubDate>Sun, 20 Sep 2026 21:27:02 +0000</pubDate>
				<category><![CDATA[Technology and Engineering]]></category>
		<category><![CDATA[air pressure]]></category>
		<category><![CDATA[bubble barrier]]></category>
		<category><![CDATA[bubble barrier effectiveness]]></category>
		<category><![CDATA[bubble curtain plastic filtration]]></category>
		<category><![CDATA[environmental engineering for plastic waste]]></category>
		<category><![CDATA[floating plastic debris removal]]></category>
		<category><![CDATA[flow hydrodynamics]]></category>
		<category><![CDATA[fluorescein tracer]]></category>
		<category><![CDATA[laboratory testing of pollution barriers]]></category>
		<category><![CDATA[low-tech plastic pollution solutions]]></category>
		<category><![CDATA[microplastic pollution]]></category>
		<category><![CDATA[microplastic retention]]></category>
		<category><![CDATA[microplastics]]></category>
		<category><![CDATA[microplastics in waterways]]></category>
		<category><![CDATA[microplastics size differentiation]]></category>
		<category><![CDATA[microplastics trapping technology]]></category>
		<category><![CDATA[particle tracking]]></category>
		<category><![CDATA[plastic particle density and buoyancy]]></category>
		<category><![CDATA[polyethylene]]></category>
		<category><![CDATA[polystyrene]]></category>
		<category><![CDATA[river plastic pollution control]]></category>
		<category><![CDATA[river pollution]]></category>
		<category><![CDATA[turbulence]]></category>
		<category><![CDATA[wastewater treatment]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=202820</guid>

					<description><![CDATA[Laboratory flume experiments reveal that air bubble barriers strongly retain large buoyant microplastics but allow small, dense particles to pass through unchanged.]]></description>
										<content:encoded><![CDATA[<p>Air bubble curtains have quickly captured the public imagination as a low-tech, chemical-free way to stop plastic pollution in rivers and harbors, but a new laboratory study provides the most detailed look yet at how these devices actually interact with the microscopic end of the plastic spectrum. The research, published in the journal Microplastics and Nanoplastics, tested a bubble barrier under carefully controlled flume conditions and found a striking split in performance: the system proved remarkably effective at trapping large, buoyant microplastics, yet largely failed to retain small, dense particles that simply rode the current past the rising wall of air. The findings offer both reassurance and a warning for engineers hoping to deploy bubble barriers as the last line of defense before rivers reach the sea.</p>
<p>The study was led by César Santos of the University of Beira Interior in Portugal, together with Marco La Capra of the University of Bayreuth, Sven Frei of Wageningen University and Research, Benjamin Gilfedder of the University of Trier, and Cristina Fael of the University of Beira Interior. Bubble barriers work by pumping compressed air through a perforated hose or diffuser laid across a waterway, generating a continuous curtain of bubbles that rises to the surface. The upward flow of air drags water with it, creating a vertical circulation cell that, in principle, deflects floating debris toward a collection point at the bank. The technology has already attracted attention in pilot projects in Europe for intercepting macroplastics, but whether it could meaningfully stem the flow of particles smaller than five millimeters remained an open question.</p>
<p>To answer it, the team built a laboratory flume experiment designed to reproduce realistic open-channel hydraulics. Flow conditions were turbulent and subcritical, with a Reynolds number of approximately 4.7 × 10³ and a Froude number of about 0.03, meaning the water was slow and deep enough that gravitational effects on the free surface were modest. They ran the bubble barrier at three air pressures, 500, 750, and 1000 mbar, and tracked two things simultaneously: how the water itself moved, and how different classes of microplastic particles traveled through the system. The hydrodynamic analysis combined velocity field measurements, including particle image velocimetry, with particle tracking techniques, giving the researchers a full picture of the turbulent structure the bubbles imposed on the water column.</p>
<p>A key innovation of the experimental design was the use of fluorescein, a fluorescent dye that acts as a conservative tracer, meaning it moves with the water without decaying or reacting. By injecting the tracer upstream and measuring breakthrough curves downstream, the team could quantify exactly how the bubble barrier changed the timing and distribution of water transport. The results were unambiguous: the barrier created both preferential flow paths, where water was channeled more quickly through certain regions, and recirculation zones, where water was trapped and recirculated in slow-moving eddies. Together, these effects extended the residence time of fluorescein in the flume by up to 24 percent, a clear demonstration that the bubble curtain fundamentally rewires local mass and momentum transfer rather than merely aerating the water.</p>
<p>Velocity contour analysis confirmed and visualized these mechanisms. The bubble stream drove strong upward convection, pulling water from the depths toward the surface and generating localized turbulence that redistributed velocities around the barrier. This vertical flow component turned out to be the crucial variable for particle capture. Naturally buoyant microplastics, represented by low-density polyethylene and high-density polyethylene, were swept upward along the rising current and accumulated at the water surface near the bubble curtain. Downstream recovery of these buoyant particles dropped to less than 20 percent, meaning that more than four-fifths of them were effectively retained by the barrier. For a passive technology that consumes only compressed air, that level of capture for floating microplastics is a significant result.</p>
<p>The picture changed dramatically for polystyrene, which is denser than water and therefore non-buoyant. The smallest polystyrene particles tested, ranging from 75 to 125 micrometers, behaved almost exactly like the fluorescein tracer. Because of their tiny size and low inertia, these particles were so strongly coupled to the surrounding flow that the turbulent structures generated by the barrier had essentially no trapping effect; downstream recoveries reached 80 percent, indicating that the vast majority sailed straight through the bubble curtain. Mid-sized particles between 200 and 400 micrometers showed moderate interaction with the barrier-induced turbulence, occupying an intermediate zone between flow-following and inertial behavior, while the largest polystyrene particles, at 600 to 1000 micrometers, were governed mainly by gravitational settling. For that largest fraction, the low downstream recovery was attributed primarily to early deposition on the flume bed rather than to retention by the barrier itself.</p>
<p>One of the most intriguing findings concerns the role of air pressure. Velocity contours measured at the higher experimental pressures revealed that strong upward convection near the bubble stream can remobilize smaller, non-buoyant microplastics that had already settled into the sediments. In other words, the same force that lifts buoyant plastics to the surface can also pluck tiny sunken particles back into the water column, where they might be exposed to further transport. This observation cuts both ways. On one hand, it suggests that carefully tuned bubble systems could help resuspend trapped microplastics and give a second chance at capturing them. On the other hand, it raises the possibility that a poorly designed barrier could re-entrain sediment-stored contamination rather than locking it away, a risk that future field deployments will need to quantify.</p>
<p>The broader significance of the study lies in its mechanistic approach. Rather than reporting a simple capture efficiency, the researchers mapped how the bubble barrier modulates the flow field and connected those hydrodynamic changes directly to particle fate. This pressure-dependent control of the local flow field is what gives bubble barriers their versatility, and also what limits them. The upward convective currents are exquisitely suited to intercepting materials with a tendency to rise, which is why the technology performs so well for buoyant polyethylene particles and for macroplastics floating at the surface. Dense, small particles, however, follow the streamlines of the flow almost perfectly, and no amount of gentle turbulence will separate them out unless the flow itself is interrupted by settling zones, filtration, or secondary treatment steps downstream.</p>
<p>The authors emphasize that the results should guide the next generation of barrier designs. To expand the technology&#8217;s reach beyond buoyant plastics, future systems will need to optimize turbulent interactions, particularly the vertical flow components, so that non-buoyant particles experience enough drag and lift to be diverted rather than bypassed. That could mean adjusting bubble density, diffuser geometry, air pressure, or even combining bubble curtains with sediment traps or collection booms that exploit the recirculation zones the barrier naturally creates. The study also highlights the value of tracer-based diagnostics: because the fluorescein breakthrough curves predicted the behavior of the smallest particles so accurately, dye tracing could become a cheap field technique for estimating whether a given barrier is likely to retain fine microplastics at a real site.</p>
<p>As concern grows over microplastic pollution in rivers, lakes, and coastal waters, and as bubble barriers move from novelty to infrastructure, this work provides a rigorous scientific foundation for deciding where the technology belongs in the treatment chain. It confirms that bubble curtains are genuine hydrodynamic tools, capable of reshaping how water and particles move through a channel, and that they can deliver impressive retention of large buoyant microplastics before runoff reaches marine environments or effluent exits wastewater treatment plants. At the same time, it delivers an honest accounting of their blind spot: the smallest, densest fragments of plastic pollution, which are also among the most abundant and hardest to remove, remain largely beyond their grasp. Closing that gap, the researchers conclude, will require refined designs that intentionally sculpt the turbulence itself, turning the invisible architecture of the flow into an active filter.</p>
<p><strong>Subject of Research:</strong> Laboratory evaluation of air bubble barrier hydrodynamics and their capacity to retain microplastic particles of varying size and buoyancy in flowing water.</p>
<p><strong>Article Title:</strong> Can bubble barriers retain microplastics? An evaluation using laboratory and hydrodynamic analysis of transport and retention</p>
<p><strong>Article References:</strong> Santos, C., La Capra, M., Frei, S., Gilfedder, B., &amp; Fael, C. (2026). Can bubble barriers retain microplastics? An evaluation using laboratory and hydrodynamic analysis of transport and retention. <em>Microplastics and Nanoplastics</em>. <a href="https://doi.org/10.1186/s43591-026-00230-4" rel="noopener noreferrer">https://doi.org/10.1186/s43591-026-00230-4</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.1186/s43591-026-00230-4" rel="noopener noreferrer">10.1186/s43591-026-00230-4</a></p>
<p><strong>Keywords:</strong> bubble barrier, microplastics, polyethylene, polystyrene, particle tracking, flow hydrodynamics, fluorescein tracer, turbulence, microplastic retention, air pressure, wastewater treatment, river pollution</p>
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		<post-id xmlns="com-wordpress:feed-additions:1">202820</post-id>	</item>
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