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	<title>surface charge &#8211; Science</title>
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	<title>surface charge &#8211; Science</title>
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		<title>Soil Minerals Decide Whether Lead Locked by Phosphorus Remediation Stays Put or Slips Away</title>
		<link>https://scienmag.com/soil-minerals-decide-whether-lead-locked-by-phosphorus-remediation-stays-put-or-slips-away/</link>
		
		<dc:creator><![CDATA[Russell Cooper]]></dc:creator>
		<pubDate>Tue, 22 Sep 2026 16:21:50 +0000</pubDate>
				<category><![CDATA[Earth Science]]></category>
		<category><![CDATA[chloropyromorphite]]></category>
		<category><![CDATA[chloropyromorphite stability]]></category>
		<category><![CDATA[colloid transport]]></category>
		<category><![CDATA[colloidal lead particles]]></category>
		<category><![CDATA[contamination mitigation strategies]]></category>
		<category><![CDATA[DLVO theory]]></category>
		<category><![CDATA[environmental fate of lead]]></category>
		<category><![CDATA[goethite]]></category>
		<category><![CDATA[heavy metal contamination]]></category>
		<category><![CDATA[heteroaggregation]]></category>
		<category><![CDATA[impact of soil minerals on pollutant stability]]></category>
		<category><![CDATA[lead immobilization in contaminated soils]]></category>
		<category><![CDATA[lead mobility in soil]]></category>
		<category><![CDATA[lead remediation]]></category>
		<category><![CDATA[lead solubility and bioavailability]]></category>
		<category><![CDATA[montmorillonite]]></category>
		<category><![CDATA[nanometer-scale mineral particles]]></category>
		<category><![CDATA[phosphorus immobilization]]></category>
		<category><![CDATA[phosphorus-based lead remediation]]></category>
		<category><![CDATA[soil chemistry and mineralogy]]></category>
		<category><![CDATA[soil colloids]]></category>
		<category><![CDATA[Soil mineral interactions]]></category>
		<category><![CDATA[surface charge]]></category>
		<category><![CDATA[water chemistry]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=206679</guid>

					<description><![CDATA[New research shows that negatively charged clay minerals can keep lead-bearing chloropyromorphite colloids mobile in soil water, while positively charged iron oxides trigger rapid aggregation and settling, reshaping how remediation sites should be assessed.]]></description>
										<content:encoded><![CDATA[<p>Phosphorus-based remediation has long been regarded as one of the most dependable strategies for dealing with lead-contaminated soils. The approach works by introducing phosphate compounds that react with lead to form chloropyromorphite, a lead phosphate mineral celebrated for its extraordinary stability and extremely low solubility. In theory, once lead is converted into this mineral, it is effectively locked in place, removed from the biologically accessible pool and prevented from migrating into groundwater, crops or the food chain. For decades, this transformation has been treated as a near-permanent fix, a chemical burial from which the toxic metal is unlikely to escape. A growing body of evidence, however, suggests that the story is considerably more complicated than solubility data alone would imply, and that particles far too small to see may hold the key to whether immobilised lead truly stays put.</p>
<p>The complication arises from the discovery that chloropyromorphite does not always remain as large, immobile crystals in treated soils. Recent studies have detected the mineral as colloidal particles, ranging in size from about one nanometre to one micrometre, in environmental matrices. Particles in this size class occupy a peculiar middle ground: they are too small to settle quickly under gravity, yet large enough to carry surface charges that govern how they interact with their surroundings. Colloids of this kind can remain suspended in water for extended periods and hitchhike on flowing pore water, potentially travelling well beyond the original contamination zone. If lead-bearing chloropyromorphite colloids can move through soil profiles, the long-term effectiveness of phosphorus remediation at a given site cannot be judged from the mineral&#8217;s low solubility alone. What matters instead is how these colloids interact with the mineral matrix that surrounds them, and that interaction is dictated largely by electrostatics.</p>
<p>A new study published in the journal Environmental Surfaces and Interfaces, led by researchers from Nanjing Normal University, has now dissected these interactions in detail. The team focused on two minerals that are almost ubiquitous in natural soils but carry opposite surface charges: montmorillonite, a negatively charged swelling clay belonging to the smectite group, and goethite, a positively charged iron oxyhydroxide that is abundant in weathered soils, particularly in tropical and subtropical regions. These two minerals were chosen because they represent the two dominant electrostatic regimes a chloropyromorphite particle is likely to encounter as it moves through different soil environments. The researchers systematically examined how each mineral affects chloropyromorphite aggregation and settling across a range of environmentally relevant conditions, varying the pH of the solution, the concentration of dissolved salts, and the type of cations present in the water.</p>
<p>The results revealed sharply contrasting behaviours. When chloropyromorphite colloids encountered montmorillonite, aggregation was significantly suppressed. The clay increased the overall negative surface charge of the suspended particles and raised the electrostatic energy barrier that normally prevents particles from approaching each other closely enough to stick. In colloidal terms, the clay acted as a stabiliser: it kept the lead-bearing particles dispersed, suspended and, crucially, mobile. Because montmorillonite is one of the most widespread clay minerals in soils worldwide, particularly in agricultural and alluvial settings, this finding carries substantial weight. A remediated site dominated by montmorillonite-rich soils may therefore allow chloropyromorphite colloids to remain in suspension and migrate laterally or vertically with percolating water, undermining the very immobilisation that phosphorus treatment was supposed to guarantee.</p>
<p>Goethite produced the opposite effect. When the iron oxide was present, chloropyromorphite colloids aggregated rapidly through a mechanism of charge neutralisation. The positively charged goethite particles attached to the negatively charged chloropyromorphite surfaces, cancelling out their repulsive charge and, in some conditions, even reversing the composite particles&#8217; charge from negative to positive. Once the energy barriers to attachment were eliminated, particles collided, fused and formed clusters large enough to settle out of suspension quickly. In practical terms, goethite acted as a natural flocculant, sweeping the lead-bearing colloids out of the water column and encouraging their retention near the source of contamination. For sites where iron oxides are abundant, this suggests a degree of natural reinforcement of the remediation outcome: the soil matrix itself helps keep the immobilised lead in place.</p>
<p>The researchers supported their observations with DLVO theory, the classical framework that describes colloidal stability as the sum of attractive van der Waals forces and repulsive electrostatic double-layer forces. The calculations confirmed the experimental picture: montmorillonite increases the interaction energy barriers between chloropyromorphite particles, stabilising the suspension, while goethite effectively eliminates those barriers, allowing rapid aggregation. This theoretical underpinning transforms the findings from isolated observations into a mechanistic understanding that can be generalised. Wherever the surface charges of the surrounding minerals either reinforce or neutralise the charge of chloropyromorphite colloids, the same aggregation behaviour should follow, providing a predictive tool for assessing sites that have not yet been measured directly.</p>
<p>Water chemistry emerged as another decisive factor. Divalent calcium ions, which are common constituents of natural waters, particularly in regions with hard water and calcareous soils, strongly promoted the aggregation of chloropyromorphite colloids. Calcium operates through two complementary mechanisms: charge screening, in which the ions compress the electrostatic double layer surrounding each particle and weaken repulsion, and cation bridging, in which a single calcium ion binds simultaneously to negatively charged surfaces on two different particles, linking them together. Both effects accelerate the formation of large aggregates and hasten settling. The implication is that in hard-water environments, even montmorillonite-dominated soils may see reduced colloid mobility, because calcium counteracts some of the clay&#8217;s stabilising influence. Conversely, in acidic, low-salt waters, electrostatic repulsion remains strong, suspensions remain stable, and the risk of colloidal lead transport rises sharply.</p>
<p>Professor Wei Wei, corresponding author of the study from the Jiangsu Engineering Lab of Water and Soil Eco-remediation at Nanjing Normal University, emphasised that the environmental fate of chloropyromorphite cannot be reduced to its chemistry as a mineral. According to Wei, the fate of the compound is strongly influenced by the surrounding mineral matrix and the chemistry of the water moving through it. In goethite-rich or hard-water environments, chloropyromorphite tends to aggregate and settle, which may help keep it immobilised at the source. But in montmorillonite-dominated or acidic, low-salt conditions, the colloids can remain highly mobile and may pose a genuine risk of off-site migration. This framing shifts the question that remediation practitioners must ask: not simply whether phosphorus treatment converts lead into chloropyromorphite, but whether the specific site conditions will allow that chloropyromorphite to remain where it formed.</p>
<p>The broader significance of the work lies in its implications for risk assessment. When phosphorus-based materials are applied to immobilise lead in contaminated soils, the durability of the treatment depends not only on the chemistry of the amendment itself but on the site-specific mineralogical composition of the soil and the hydrochemistry of the site. Effective long-term evaluation, the researchers argue, must account for soil type, water hardness and pH. A site assessment that relies solely on total lead concentrations or on the assumed insolubility of chloropyromorphite may dramatically underestimate the mobility of lead in clay-rich, acidic, soft-water environments, while overestimating risk in iron-oxide-rich or hard-water settings. As phosphorus remediation continues to be deployed at industrial legacy sites, shooting ranges, urban brownfields and former battery-recycling areas worldwide, these findings offer a practical framework: characterise the colloidal mineralogy and water chemistry of the site, apply DLVO-based reasoning to predict colloid stability, and tailor monitoring strategies accordingly. In doing so, the study converts a seemingly paradoxical observation, that a highly insoluble mineral can still transport its toxic payload, into a manageable set of predictive principles, strengthening the scientific basis on which the long-term safety of lead remediation can be judged.</p>
<p><strong>Subject of Research:</strong> Surface charge-mediated heteroaggregation of chloropyromorphite colloids with natural soil minerals and its implications for lead remediation</p>
<p><strong>Article Title:</strong> Surface charge-mediated heteroaggregation of chloropyromorphite with natural inorganic colloids: Mechanisms and remediation implications</p>
<p><strong>Article References:</strong> Surface charge-mediated heteroaggregation of chloropyromorphite with natural inorganic colloids: Mechanisms and remediation implications. (n.d.). <a href="https://www.eurekalert.org/news-releases/1144776" 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> chloropyromorphite, lead remediation, soil colloids, montmorillonite, goethite, heteroaggregation, DLVO theory, surface charge, colloid transport, heavy metal contamination, phosphorus immobilization, water chemistry</p>
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		<post-id xmlns="com-wordpress:feed-additions:1">206679</post-id>	</item>
		<item>
		<title>Parasite Eggs and Cysts Carry Negative Charges That May Undermine Diagnosis</title>
		<link>https://scienmag.com/parasite-eggs-and-cysts-carry-negative-charges-that-may-undermine-diagnosis/</link>
		
		<dc:creator><![CDATA[Ophelia Keating]]></dc:creator>
		<pubDate>Sat, 12 Sep 2026 00:32:48 +0000</pubDate>
				<category><![CDATA[Biology]]></category>
		<category><![CDATA[Ascaris lumbricoides]]></category>
		<category><![CDATA[Brazilian research on parasite surface properties]]></category>
		<category><![CDATA[effect of negative surface charges on parasitology diagnostics]]></category>
		<category><![CDATA[electrical properties of parasite eggs and cysts]]></category>
		<category><![CDATA[electrophoretic mobility]]></category>
		<category><![CDATA[fecal samples]]></category>
		<category><![CDATA[flotation]]></category>
		<category><![CDATA[Giardia duodenalis]]></category>
		<category><![CDATA[hydrophobicity]]></category>
		<category><![CDATA[impact of parasite surface charge on diagnostic methods]]></category>
		<category><![CDATA[implications for parasitic disease diagnosis]]></category>
		<category><![CDATA[influence of surface charge on parasite detection accuracy]]></category>
		<category><![CDATA[intestinal parasite detection challenges]]></category>
		<category><![CDATA[negative electrical charge on parasite cysts]]></category>
		<category><![CDATA[parasite diagnosis]]></category>
		<category><![CDATA[parasitic egg surface charge]]></category>
		<category><![CDATA[parasitic infections and laboratory testing]]></category>
		<category><![CDATA[parasitology]]></category>
		<category><![CDATA[sedimentation]]></category>
		<category><![CDATA[surface charge]]></category>
		<category><![CDATA[surface charge measurement of intestinal parasites]]></category>
		<category><![CDATA[Taenia]]></category>
		<category><![CDATA[zeta potential]]></category>
		<category><![CDATA[zeta potential in parasitology]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=193246</guid>

					<description><![CDATA[Researchers have measured negative zeta potentials on Ascaris lumbricoides eggs, Giardia duodenalis cysts, and Taenia eggs from preserved human fecal samples, suggesting electrostatic forces may compromise standard parasite diagnostic techniques.]]></description>
										<content:encoded><![CDATA[<p>Intestinal parasitic infections remain one of the most widespread public health burdens on the planet, and the laboratory techniques used to detect them have changed remarkably little over decades. Now, a team of Brazilian researchers has measured, for the first time, the electrical charge on the surfaces of three of the world&#8217;s most common intestinal parasites—<i>Ascaris lumbricoides</i>, <i>Giardia duodenalis</i>, and <i>Taenia</i> species—directly from preserved human fecal samples. Their findings, published in <i>Acta Parasitologica</i>, reveal that all three parasite structures carry strong negative surface charges, a physical property that the authors argue may be quietly sabotaging the very diagnostic methods laboratories rely on every day.</p>
<p>The study, led by Quéren Hapuque de Castro Novelli of the University of Campinas in São Paulo, together with colleagues from ImmunoCamp Science and Technology, the Adolfo Lutz Institute, and other Brazilian institutions, focused on a quantity known as the zeta potential. This is a measure of the electrical potential at the slipping plane surrounding a suspended particle, and it governs how particles interact with each other and with their chemical environment. When two surfaces carry like charges, they repel; when their charges are opposite, they attract. For parasite eggs, cysts, and oocysts suspended in fecal material, these electrostatic forces can determine whether the structures sediment to the bottom of a tube, float to the surface of a dense solution, bind to debris, or drift uselessly out of the operator&#8217;s field of view.</p>
<p>Standard diagnostic protocols for intestinal parasites—spontaneous sedimentation, centrifugal sedimentation using formalin with ether or ethyl acetate, and flotation techniques based on zinc sulfate, sodium chloride, or sucrose solutions—are designed around a single physical property: the density of the parasite structure. Yet the researchers point out that these methods largely ignore electrostatic forces and the inherent hydrophobicity of parasite surfaces, factors that can reduce recovery efficiency and contribute to the low-to-moderate sensitivity that plagues routine parasitology. The motivation for the new work was to quantify this neglected variable in structures taken directly, or in natura, from preserved fecal samples rather than from laboratory-cultured parasites under idealized conditions.</p>
<p>To obtain clean parasite material, the team screened samples submitted to the Ouro Verde Hospital Municipal Laboratory of Campinas, selecting those that tested positive with high infection intensity by the Kato-Katz method. The samples, preserved in 7.5 percent buffered formalin, were filtered through 400 and 200 micrometer meshes and then subjected to repeated cycles of dilution in deionized water and centrifugation at 490 times gravity for five minutes, a process repeated five times to strip away fecal debris and concentrate the parasite structures. Under a stereomicroscope, individual eggs and cysts were then captured with a 10 microliter micropipette and transferred to fresh tubes, a meticulous manual procedure repeated six times that ultimately yielded approximately 400 helminth eggs and more than 1,000 protozoan cysts completely free of contaminating fecal material.</p>
<p>Surface charge was then measured with a Malvern Zetasizer Nano ZS, an instrument that determines zeta potential from electrophoretic mobility. An electric field is applied across the sample cell, inducing charged particles to move at speeds proportional to their charge density. The instrument tracks this motion by analyzing Doppler shifts in laser light scattered by the moving particles: faster-moving particles produce larger frequency shifts, and from these shifts the electrophoretic mobility and the zeta potential are calculated. Each sample was analyzed in triplicate, and the instrument&#8217;s software classified every measurement as good quality, ruling out artifacts from bubbles, viscosity, or inadequate particle concentration.</p>
<p>The results were unambiguous. All three parasite species carried net negative surface charges, with values ranging across samples from −14.2 to −32.1 millivolts. <i>Giardia duodenalis</i> cysts proved the most strongly charged, averaging −28 millivolts, while <i>Ascaris lumbricoides</i> eggs averaged −21.9 millivolts and <i>Taenia</i> species eggs averaged −18.4 millivolts. Statistical comparison across species groups using ANOVA confirmed the significance of the measurements. Notably, this is the first study ever to report the surface charge of <i>Ascaris lumbricoides</i> and <i>Taenia</i> eggs, filling a long-standing gap in the physicochemical characterization of these globally important pathogens.</p>
<p>The findings align closely with earlier work on related organisms studied under controlled conditions. Previous research found that <i>Cryptosporidium</i> oocysts carry surface charges of around −38 to −40 millivolts and <i>Giardia</i> cysts around −17 to −35 millivolts, with charge becoming less negative as the surrounding medium grows more acidic. Studies of <i>Ascaris suum</i> eggs have shown that more than 70 percent of the egg surface is hydrophobic, a property explained by electron microscopy studies revealing the egg&#8217;s layered architecture: an outer proteinaceous membrane, a middle chitin layer, and an inner lipid layer. That layered composition likely underlies the negative charge and hydrophobic character observed in the present study as well.</p>
<p>The clinical significance of these numbers becomes clear when placed in the context of known diagnostic failures. The authors cite work on the formalin-ether concentration procedure showing that even when centrifugation force, time, solvents, and surfactants were systematically optimized, certain parasite species stubbornly resisted sedimentation—as though an invisible chemical force were acting against their movement through the suspension. The zeta potential measurements now provide a candidate explanation: repulsive electrostatic interactions between the negatively charged parasite surfaces and the surrounding medium or other negatively charged fecal particles can oppose the gravitational and density-driven forces on which sedimentation and flotation depend, keeping eggs and cysts suspended and out of the diagnostic sediment.</p>
<p>Understanding these surface properties also points toward solutions. One proposed alternative technique, dissolved air flotation, exploits surface charge directly by using carrier molecules adsorbed onto air bubbles to capture oppositely charged particles, which then rise to the surface for collection. Similar electrostatic logic underpins the successful use of paramagnetic microspheres to isolate <i>Schistosoma mansoni</i> eggs from feces and of immunomagnetic particles to capture <i>Cryptosporidium</i> oocysts. The authors suggest that ionic compounds capable of reducing the repulsive charges in fecal suspensions could replace some of the harsh and hazardous reagents currently used—saturated salt solutions that damage parasite morphology, and volatile solvents such as ether and ethyl acetate that pose risks to laboratory workers and the environment. Evidence from malaria research reinforces the principle: red blood cells infected with <i>Plasmodium falciparum</i> trophozoites exhibit a zeta potential of −14.6 millivolts, significantly lower than uninfected cells, promoting the cytoadherence that is central to the disease&#8217;s pathology.</p>
<p>Beyond improving today&#8217;s diagnostic protocols, the researchers argue that these first quantitative surface-charge data for <i>Ascaris</i> and <i>Taenia</i> eggs open the door to an entirely new generation of tools, including engineered nanoparticles designed to bind specifically to enteric pathogens based on their electrochemical signatures. In an era when intestinal parasites still disproportionately affect communities with poor sanitation, and when preventive chemotherapy faces the growing threat of anthelmintic resistance, even modest gains in diagnostic sensitivity could translate into meaningful public health benefits. By revealing the hidden electrostatic forces at play inside a routine stool specimen, this study gives laboratory scientists a physical parameter they have largely ignored for decades—and a concrete target for the diagnostic methods of the future.</p>
<p>The choice of formalin as a preservative deserves particular attention when interpreting these measurements. Buffered formalin has been the workhorse preservative of parasitology laboratories for generations because it fixes parasite morphology and halts decay without requiring refrigeration, making it practical in resource-limited settings where most infections occur. Yet fixatives can alter surface chemistry, cross-linking membrane proteins and changing the ionizable groups exposed at the particle surface. The fact that robust negative charges persisted even after formalin fixation suggests that the electrostatic character of these structures is stable and intrinsic, but it also means that measurements from fresh, unfixed specimens remain an open question for future work.</p>
<p>The zeta potential itself is not a direct reading of the membrane charge but an indirect inference made at the slipping plane, the boundary between the tightly bound ion layer around a particle and the diffuse layer that moves with it under an electric field. This is why factors such as ionic strength, pH, and temperature of the suspending medium all influence the measured value. The deionized water and dilute formalin used here create a low-conductivity environment that favors clean electrophoretic measurements, but real fecal suspensions are far more chemically complex, rich in bile salts, fatty acids, and electrolytes that can screen or modify surface charges. Translating these clean measurements to the messy reality of a diagnostic suspension is the next conceptual step.</p>
<p>The public health stakes are considerable. Soil-transmitted helminths such as <i>Ascaris lumbricoides</i> infect hundreds of millions of people worldwide, and <i>Giardia duodenalis</i> is among the most frequently identified causes of diarrheal illness in children in low-income regions. World Health Organization deworming programs depend on diagnostic stool examination both to map infection prevalence and to monitor the impact of mass drug administration, yet the modest sensitivity of conventional concentration techniques means true infection burdens are likely underestimated, particularly for light infections that fall below the detection threshold of a single slide.</p>
<p>There is also a methodological legacy worth noting: the sedimentation and flotation techniques in routine use today descend largely from methods formalized in the early twentieth century, refined empirically long before particle electrophoresis became accessible to parasitology laboratories. The present study exemplifies a broader trend of importing characterization tools from colloid science and environmental engineering into medical parasitology, a convergence that previously proved fruitful in water treatment research on <i>Cryptosporidium</i> and <i>Giardia</i>, where surface charge informed the design of filtration and coagulation processes for drinking water safety.</p>
<p><strong>Subject of Research:</strong> Measurement of surface zeta potential charges of intestinal parasite eggs and cysts in preserved fecal samples and their impact on diagnostic separation techniques</p>
<p><strong>Article Title:</strong> The Evaluation of Surface Charges of Ascaris Lumbricoides, Giardia Duodenalis, and Taenia spp., in Preserved Fecal Samples Processed in Natura</p>
<p><strong>Article References:</strong> de Castro Novelli, Q. H., Soares, F. A., Margatho, V. S., Fernandes, E. P., Suzuki, C. T. N., Sabadini, E., dos Santos, B. M., de Melo, L. C. V., de Oliveira Baccin, A., Falcão, A. X., &amp; Gomes, J. F. (2026). The Evaluation of Surface Charges of Ascaris Lumbricoides, Giardia Duodenalis, and Taenia spp., in Preserved Fecal Samples Processed in Natura. <em>Acta Parasitologica, 71</em>(5), Article 209. <a href="https://doi.org/10.1007/s11686-026-01367-1" rel="noopener noreferrer">https://doi.org/10.1007/s11686-026-01367-1</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.1007/s11686-026-01367-1" rel="noopener noreferrer">10.1007/s11686-026-01367-1</a></p>
<p><strong>Keywords:</strong> Ascaris lumbricoides, Giardia duodenalis, Taenia, zeta potential, surface charge, parasite diagnosis, fecal samples, sedimentation, flotation, electrophoretic mobility, hydrophobicity, parasitology</p>
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