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	<title>mineralization &#8211; Science</title>
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	<link>https://scienmag.com</link>
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	<title>mineralization &#8211; Science</title>
	<link>https://scienmag.com</link>
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		<title>Scientists Set the Bar for What Counts as a Real Bone Organoid</title>
		<link>https://scienmag.com/scientists-set-the-bar-for-what-counts-as-a-real-bone-organoid/</link>
		
		<dc:creator><![CDATA[Gregory Coleman]]></dc:creator>
		<pubDate>Fri, 25 Sep 2026 22:39:40 +0000</pubDate>
				<category><![CDATA[Technology and Engineering]]></category>
		<category><![CDATA[advances in bone organoid research]]></category>
		<category><![CDATA[bioinks]]></category>
		<category><![CDATA[bioprinting]]></category>
		<category><![CDATA[bone organoids]]></category>
		<category><![CDATA[bone regeneration]]></category>
		<category><![CDATA[bone remodeling in vitro]]></category>
		<category><![CDATA[Bone tissue engineering]]></category>
		<category><![CDATA[challenges in bone organoid development]]></category>
		<category><![CDATA[criteria for authentic bone organoids]]></category>
		<category><![CDATA[Disease Modeling]]></category>
		<category><![CDATA[drug screening]]></category>
		<category><![CDATA[hydrogels]]></category>
		<category><![CDATA[innervation in bone models]]></category>
		<category><![CDATA[limitations of current bone models]]></category>
		<category><![CDATA[mechanically active tissue recreation]]></category>
		<category><![CDATA[mineralization]]></category>
		<category><![CDATA[mineralized tissue modeling]]></category>
		<category><![CDATA[operational definition of bone organoids]]></category>
		<category><![CDATA[organoid classification]]></category>
		<category><![CDATA[osteoblasts]]></category>
		<category><![CDATA[osteoclasts]]></category>
		<category><![CDATA[scaffold-free bone tissue models]]></category>
		<category><![CDATA[vascularization]]></category>
		<category><![CDATA[vascularization in bone organoids]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=215048</guid>

					<description><![CDATA[A new review in Materials Today Bio proposes the first operational definition of a bone organoid and finds that most current models fall short of the label, offering a five-tier classification, a bioprinting evidence audit and a reporting checklist to standardize the fast-growing field.]]></description>
										<content:encoded><![CDATA[<p>Bone has long been the stubborn cousin of organoid science. While researchers have grown miniature guts, brains, kidneys and livers in dishes for over a decade, the skeleton has resisted the same treatment, because bone is not simply a collection of cells in three dimensions. It is a mineralized, mechanically active, continuously remodeled, vascularized and innervated tissue, and methods developed for soft epithelial organoids cannot be transferred to it without accounting for stiffness, load transmission, oxygen delivery and the slow transition from immature matrix to hardened tissue. Now a comprehensive review published in Materials Today Bio by Yining Huang, Tianlong Zhang and colleagues offers the field something it has conspicuously lacked: a rigorous operational definition of what a bone organoid actually is, and an honest audit of how close current models come to meeting it.</p>
<p>The authors argue that the term bone organoid has been applied far too loosely. Spheroids, which are useful modular building blocks that can enhance osteogenic differentiation, often lack tissue-level organization altogether. Engineered constructs can reproduce geometry or mechanical behavior yet remain dominated by an exogenous scaffold rather than by cells. Under the framework proposed in the review, a genuine bone organoid must satisfy four core criteria: it must be a viable cell-derived three-dimensional tissue that develops organization beyond simple aggregation; it must produce its own collagenous or osteoid-like matrix with spatially and temporally resolved mineralization; it must show that new mineral is biologically deposited rather than inherited from the material it was grown on; and it must display at least one dynamic skeletal function, such as regulated matrix formation, formation-resorption coupling or a controlled mechanobiological response. Engineered guidance is permitted, but only when it is transient or demonstrably permissive to endogenous organization.</p>
<p>The review goes further by proposing a tiered classification system with five categories: osteogenic spheroids, bone-like microtissues, engineered skeletal constructs, bone organoids and high-fidelity bone organoids. The top designation demands evidence across three interdependent domains. Structural mimicry requires hierarchical extracellular matrix organization and progressive mineralization that mirrors the sequence seen in native bone, where cells first deposit unmineralized osteoid and mineral then advances from discrete fronts. Functional fidelity requires coupled activity between osteoblast-lineage cells that build matrix and osteoclast-lineage cells that resorb it, linked through signaling pathways such as RANKL, RANK and osteoprotegerin. Biomechanical integrity requires that the construct maintain structural coherence and exhibit measurable mechanosensation, reflecting the fact that bone cells continuously convert mechanical loading, fluid flow and matrix stiffness into biological responses. Crucially, the authors stress that a sophisticated scaffold-dominated construct can be clinically useful while still falling outside the organoid class; placement is a statement about the source of organization, not about quality.</p>
<p>When the authors applied this classification to representative original studies, the results were sobering. Of the ten studies examined in their evidence map, several constructs labeled organoids by their original authors were reassigned as osteogenic spheroids because self-assembly was limited to the spheroid unit and tissue-level hierarchy was never demonstrated. Others were reclassified as engineered skeletal constructs because pre-existing material architecture dominated organization. Only a handful, including a 2021 woven bone organoid grown from human bone marrow stromal cells and a 2025 system using dynamic dual-network hydrogels in which cell migration generated spatiotemporal woven-bone architecture, met the core organoid criteria. Notably, no current model satisfies every high-fidelity domain, and the reviewers conclude that transparent reporting of what was tested, and what was not, is essential for the field to advance.</p>
<p>A recurring problem the review highlights is confounding between biological mineralization and material-derived mineral signals. Many popular bone engineering strategies incorporate nano-hydroxyapatite, bioactive glass or black-phosphorus nanosheets that release phosphate ions, and any of these can generate calcium deposits that look like bone formation on a stain but are actually chemical precipitation. The framework therefore demands that active, biologically regulated mineralization be distinguished from material contributions using acellular baselines, a requirement that several widely cited nanomaterial-based studies do not currently meet. The authors also emphasize that late osteogenic marker expression alone does not establish functional bone-like tissue; marker data must be interpreted alongside matrix organization and mineral distribution.</p>
<p>Beyond classification, the review provides a detailed account of the biology that a faithful model must capture. Osteoblasts deposit type I collagen-rich osteoid that later mineralizes as hydroxyapatite crystals grow; a subset of these cells becomes embedded as osteocytes, which sense strain through dendritic processes in canalicular networks and regulate both building and resorption through mediators such as sclerostin. Osteoclasts, formed by fusion of monocyte-macrophage precursors, acidify the resorption compartment and release enzymes that remove mineral and collagen while also releasing matrix-stored growth factors like TGF-beta and BMP-related signals. Meanwhile, endothelial cells provide angiocrine signaling that supports osteoprogenitor maintenance, and neural elements release calcitonin gene-related peptide and substance P, which influence osteoblast, osteoclast and vascular function. The review cautions that multilineage marker expression alone is insufficient; functional integration must be demonstrated with lineage-appropriate readouts such as lumen formation and perfusion for vessels, or innervation-dependent regulation of remodeling for nerves.</p>
<p>On the fabrication side, the authors take a clear-eyed view of bioprinting, distinguishing between printing preformed organoids and printing for organoid formation, with only the former deserving the label unless post-print self-organization is demonstrated. They survey the four major modalities: inkjet printing offers fine patterning but limited viscosity range, extrusion printing handles mineral-filled bioinks and is the most scalable but exposes cells to shear stress, laser-assisted printing achieves micrometer-scale nozzle-free patterning but is limited by throughput, and light-based stereolithography and digital light processing generate complex channels but suffer from optical attenuation in mineral-rich inks. Across all modalities, the review finds that evidence that printing improves organoid maturation remains substantially weaker than evidence that it improves initial geometry. Hybrid strategies, such as temporary scaffold-guided self-assembly, printed channels coupled with self-organized microvasculature, and modular assembly of developmentally primed cartilage microtissues, are highlighted as the most promising path forward, exemplified by recent bioprinted bone-organoid grafts with guided vascularization that matured after implantation.</p>
<p>The translational outlook is cautiously encouraging. Patient-derived chondrosarcoma organoids have faithfully recapitulated histological and genetic features of parental tumors and shown sensitivity to the SHH pathway inhibitor vismodegib, while a biobank of 44 sarcoma organoid lines has enabled high-throughput drug screening. A three-dimensional vascularized humanized bone organoid has revealed that estrogen withdrawal drives vessel-like structure formation and mineral deposition, offering mechanistic insight into postmenopausal osteoporosis that non-vascularized models could not capture. Induced pluripotent stem cell-derived jawbone organoids have reproduced phenotypic features of osteogenesis imperfecta, pointing toward precision modeling of genetic skeletal disease. For regenerative applications, engineered ossification center-like organoids and periosteum-derived organoids combined with printed scaffolds have achieved bone repair in rodent critical-sized defects, though the authors note that systematic comparison against autograft controls remains an essential next step.</p>
<p>The review closes with a series of practical proposals intended to move the field from anecdote to standard. These include a minimum reporting checklist covering cell source, passage number, matrix composition, induction schedules, regional rather than whole-construct viability, quantitative mineralization assessment and predefined exclusion criteria for poorly formed organoids, together with application-specific potency assays: coupled remodeling endpoints for osteoporosis models, reproducible dose-response data for drug screening platforms and vascularized bone formation for regenerative grafts. The authors also flag regulatory hurdles, noting that clinical-grade organoids will require good manufacturing practice compliance, validated potency assays and jurisdiction-specific pathways such as the European Advanced Therapy Medicinal Product framework. Their overarching message is that progress will come not from adding complexity indiscriminately but from controlling when and where complexity is introduced, with stimuli-responsive matrices that yield to endogenous tissue, machine-learning-optimized printing and microfluidic platforms that connect bone organoids to vascular, immune and metabolic modules. Bone organoids, the review concludes, occupy a genuinely valuable intermediate position between dish and animal, provided the label is reserved for constructs that can prove they deserve it.</p>
<p><strong>Subject of Research:</strong> Development of an operational classification framework and biofabrication standards for engineering high-fidelity bone organoids</p>
<p><strong>Article Title:</strong> Engineering high-fidelity bone organoids: Operational classification, multilineage crosstalk, biofabrication evidence, and translational validation</p>
<p><strong>Article References:</strong> Huang, Y., Zhang, T., Chen, S., Zhou, H., Xu, H., Zhang, F., Li, L., &amp; Lyu, F. (2026). Engineering high-fidelity bone organoids: Operational classification, multilineage crosstalk, biofabrication evidence, and translational validation. <em>Materials Today Bio, 41</em>, Article 103676. <a href="https://doi.org/10.1016/j.mtbio.2026.103676" rel="noopener noreferrer">https://doi.org/10.1016/j.mtbio.2026.103676</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.1016/j.mtbio.2026.103676" rel="noopener noreferrer">10.1016/j.mtbio.2026.103676</a></p>
<p><strong>Keywords:</strong> bone organoids, organoid classification, bioprinting, osteoblasts, osteoclasts, mineralization, vascularization, hydrogels, disease modeling, drug screening, bone regeneration, bioinks</p>
]]></content:encoded>
					
		
		
		<post-id xmlns="com-wordpress:feed-additions:1">215048</post-id>	</item>
		<item>
		<title>How MoS2 Heterojunction Band Alignment Controls Sunlight-Driven Dye Breakdown</title>
		<link>https://scienmag.com/how-mos2-heterojunction-band-alignment-controls-sunlight-driven-dye-breakdown/</link>
		
		<dc:creator><![CDATA[Bethany Barker]]></dc:creator>
		<pubDate>Tue, 22 Sep 2026 14:06:24 +0000</pubDate>
				<category><![CDATA[Chemistry]]></category>
		<category><![CDATA[1T phase]]></category>
		<category><![CDATA[2H phase]]></category>
		<category><![CDATA[advanced oxidation processes]]></category>
		<category><![CDATA[aromatic amines from azo dyes]]></category>
		<category><![CDATA[atomically thin 2D materials for pollution control]]></category>
		<category><![CDATA[band alignment]]></category>
		<category><![CDATA[dye degradation]]></category>
		<category><![CDATA[environmental impact of synthetic dyes]]></category>
		<category><![CDATA[Heterojunctions]]></category>
		<category><![CDATA[interfacial charge transfer in MoS2 heterostructures]]></category>
		<category><![CDATA[mechanistic insights into MoS2-based photocatalysts]]></category>
		<category><![CDATA[mineralization]]></category>
		<category><![CDATA[MoS2]]></category>
		<category><![CDATA[MoS2 heterojunction band alignment]]></category>
		<category><![CDATA[Photocatalysis]]></category>
		<category><![CDATA[reactive oxygen species]]></category>
		<category><![CDATA[reactive oxygen species generation in photocatalysis]]></category>
		<category><![CDATA[role of MoS2 in]]></category>
		<category><![CDATA[sulfur vacancies]]></category>
		<category><![CDATA[sunlight-driven dye degradation]]></category>
		<category><![CDATA[type-I and type-II heterojunctions in MoS2]]></category>
		<category><![CDATA[wastewater treatment]]></category>
		<category><![CDATA[water pollution from industrial dye wastewater]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=205643</guid>

					<description><![CDATA[A new review reveals how Type-I and Type-II band alignments in MoS2 heterojunctions dictate charge separation, radical generation, and the real-world limits of sunlight-driven dye degradation.]]></description>
										<content:encoded><![CDATA[<p>Synthetic dyes have become one of the most stubborn signatures of industrial civilization. Global dye production now exceeds one million tons every year, and roughly 280,000 tons of that output escapes into wastewater streams, driven largely by reactive dyeing processes in which as much as half of the colorant never bonds to the fabric. Because even concentrations as low as 0.005 milligrams per liter are visible to the naked eye, these pollutants discolor rivers, block light from penetrating water columns, choke photosynthesis, and deplete dissolved oxygen. Worse, certain dye classes, particularly azo dyes and nitrated polycyclic aromatic compounds, can transform into aromatic amines, compounds associated with skin irritation, respiratory disorders, and even bladder cancer. A new open-access review published in Discover Green Chemistry argues that the answer to this persistent problem may lie in an atomically thin material that most people know from lubricants and electronics: molybdenum disulfide, or MoS₂.</p>
<p>The review, written by Sirajudheen Palliyalil, Nabeena Chettithodi Poovathumkuzhi, and Sivakumar Vigneshwaran, delivers something the field has lacked: a unified mechanistic framework linking band alignment, interfacial charge migration, and reactive oxygen species generation in MoS₂-based Type-I and Type-II heterojunctions. Rather than cataloging degradation percentages, the authors systematically connect how electrons and holes move across semiconductor interfaces with which radicals actually attack dye molecules. This matters because photocatalysis, an advanced oxidation process that uses light-activated semiconductors to generate hydroxyl and superoxide radicals, is one of the few technologies capable of both degrading and completely mineralizing organic pollutants without merely shuffling them from water into sludge, the chief failing of adsorption, coagulation, and membrane methods.</p>
<p>The appeal of MoS₂ begins with its structure. As a member of the transition metal dichalcogenide family, it consists of atomically thin S–Mo–S layers stacked by weak van der Waals forces, allowing exfoliation into monolayers. Thinning the material transforms its electronics dramatically: bulk MoS₂ is an indirect-gap semiconductor with a band gap near 1.2 electron volts, while the monolayer form is a direct-gap semiconductor at roughly 1.9 electron volts, sharply improving visible-light absorption. The material also comes in three crystalline polymorphs. The semiconducting 2H phase, thermodynamically stable with trigonal prismatic coordination, absorbs light but suffers from modest conductivity around 10⁻⁴ S cm⁻¹ and correspondingly rapid electron–hole recombination. The metallic 1T phase, with octahedral coordination, conducts electricity up to a million times better and serves as an electron relay. The rarer rhombohedral 3R phase offers anisotropic charge transport but remains hard to synthesize in phase-pure form. Mixed-phase 1T/2H systems exploit this complementarity: with the metallic phase acting as a charge sink, interfacial resistance in engineered systems has dropped from roughly 9 ohms to 0.4 ohms, photocurrents have climbed to 140–180 microamperes per square centimeter, and degradation efficiencies have jumped from the 9–72 percent range for pure 2H material to 95–99 percent in optimized hybrids.</p>
<p>Defect engineering adds another layer of control. Sulfur vacancies, sitting 0.1 to 0.4 electron volts below the conduction band, act as shallow electron traps that suppress recombination, strengthen oxygen binding, and facilitate superoxide radical formation. Density functional theory studies cited in the review show that vacancies and antisite defects create donor-like states that lower the activation energy for electronic transitions. Moderate defect densities can lift degradation efficiency from around 50–60 percent to over 80–95 percent, but the relationship is nonlinear: excessive vacancies create deep trap states that become recombination centers. Precision, the authors stress, is everything.</p>
<p>The heart of the review is its comparative analysis of the two fundamental heterojunction architectures. In a Type-I, or straddling-gap, junction, the conduction and valence band edges of one semiconductor lie entirely within those of its partner, typically MoS₂. Photogenerated electrons and holes both migrate into the narrow-gap material and accumulate there. This preserves relatively strong redox potentials but concentrates charges in a single phase, producing intense photoluminescence, low photocurrents of roughly 0.5–2 microamperes per square centimeter, quantum efficiencies near 1–2 percent, and weak generation of hydroxyl radicals. The thermodynamic problem is stark: MoS₂&#8217;s valence band sits near +1.6 volts versus the normal hydrogen electrode, below the +1.99 volt threshold needed to oxidize water directly into hydroxyl radicals. Type-I systems therefore tend to rely on superoxide-dominated, single-pathway degradation, which scavenger experiments confirm with suppression rates exceeding 80 percent when benzoquinone is added and minimal response to isopropanol.</p>
<p>Type-II, or staggered-gap, junctions take the opposite approach. Band offsets of roughly 0.2 to 1.0 electron volts push electrons toward the lower conduction band and holes toward the higher valence band, spatially separating charge across the interface. Photoluminescence is strongly quenched, electrochemical impedance shrinks, and degradation efficiencies routinely exceed 90 percent, as in MoS₂–Bi₂O₃ systems that eliminate 95 percent of methylene blue in 30 minutes. Yet the review is careful to highlight the hidden cost: as carriers relax into less energetic band edges, redox driving force diminishes. The authors illustrate this with a MoS₂/MoO₃ junction in which the conduction band of MoO₃ at −0.12 volts is too positive for superoxide generation, which requires potentials below −0.33 volts, and the MoS₂ valence band is far too negative for direct hydroxyl radical formation. Efficient charge separation alone, they conclude, cannot guarantee radical production; band-edge thermodynamics impose constraints that no interface can engineer away entirely.</p>
<p>To validate these mechanisms, the review critically evaluates the spectroscopic toolkit that modern photocatalysis demands. UV–Vis diffuse reflectance spectroscopy, processed through the Kubelka–Munk function and Tauc plots, reveals band-gap narrowing; in MoS₂/g-C₃N₄ composites, gaps shrink from 2.61 electron volts in the bare polymer to 2.32 and 2.26 electron volts in the hybrids, confirming enhanced visible-light harvesting. Photoluminescence quenching quantifies recombination suppression, while electrochemical impedance spectroscopy and Mott–Schottky analysis expose charge-transfer resistance and flat-band potentials. X-ray and ultraviolet photoelectron spectroscopy pin down absolute band positions, and electron paramagnetic resonance with DMPO spin traps directly identifies superoxide and hydroxyl radicals, showing the characteristic multi-radical signature of Type-II systems against the electron-dominated profile of Type-I. Langmuir–Hinshelwood kinetics and chemical oxygen demand and total organic carbon measurements then translate these electronic insights into real degradation performance.</p>
<p>The review does not shy away from the field&#8217;s most uncomfortable numbers. In simulated solutions, MoS₂-based catalysts achieve near-total mineralization; a chitosan/MoS₂/graphene oxide membrane reached 100 percent total organic carbon removal of methyl orange, and a Co₃O₄/MoS₂ composite degraded 97 percent of rhodamine B within five minutes. In real wastewater, performance collapses. Sulfadiazine degradation fell from 99 percent in deionized water to roughly 49–59 percent in tap, lake, and river water; industrial effluent treatment achieved only 65 percent chemical oxygen demand and about 52 percent total organic carbon removal after 150 minutes. Competing anions scavenge reactive oxygen species, suspended solids attenuate light, and natural organic matter fouls active sites. Reusability tells a similar cautionary tale: although well-engineered composites retain 85–95 percent activity over several cycles, long-term operation invites photocorrosion, oxidation of Mo⁴⁺, and the metastable 1T phase reverting to 2H, silently eroding the conductive pathways that made the catalyst effective.</p>
<p>The authors&#8217; prescriptions are correspondingly practical. Hydrothermal and solvothermal routes, which promote intimate interfacial contact and staggered band alignment, favor Type-II architectures; in situ growth reduces interfacial defects; protective carbon coatings, magnetic functionalization with Fe₃O₄ for easy recovery, and careful phase balancing extend operational lifetimes. Operational parameters, catalyst dosage, dye concentration, pH, irradiation intensity, and time, are interdependent variables that must be co-optimized rather than tuned in isolation. Above all, the review calls for systematic testing in authentic wastewater matrices, arguing that laboratory results from synthetic dye solutions systematically overestimate real-world performance. For a technology whose promise rests on using free sunlight to turn persistent pollutants into carbon dioxide and water, that honest reckoning with the gap between bench and river may prove as valuable as any single catalyst design. The framework the authors provide, connecting band alignment to radical generation to mineralization, gives researchers a rational map for building the next generation of MoS₂ photocatalysts that can finally close it.</p>
<p><strong>Subject of Research:</strong> Mechanistic study of Type-I and Type-II MoS2 heterojunction photocatalysts for the degradation of organic dyes in wastewater.</p>
<p><strong>Article Title:</strong> Mechanistic insights into Type-I and Type-II MoS₂ heterojunctions for the photodegradation of organic dyes</p>
<p><strong>Article References:</strong> Palliyalil, S., Poovathumkuzhi, N. C., &amp; Vigneshwaran, S. (2026). Mechanistic insights into Type-I and Type-II MoS₂ heterojunctions for the photodegradation of organic dyes. <em>Discover Green Chemistry, 1</em>(1), Article 18. <a href="https://doi.org/10.1007/s44509-026-00020-4" rel="noopener noreferrer">https://doi.org/10.1007/s44509-026-00020-4</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.1007/s44509-026-00020-4" rel="noopener noreferrer">10.1007/s44509-026-00020-4</a></p>
<p><strong>Keywords:</strong> MoS2, photocatalysis, heterojunctions, dye degradation, reactive oxygen species, wastewater treatment, band alignment, 2H phase, 1T phase, advanced oxidation processes, sulfur vacancies, mineralization</p>
]]></content:encoded>
					
		
		
		<post-id xmlns="com-wordpress:feed-additions:1">205643</post-id>	</item>
		<item>
		<title>Plant-Powered Nanocatalyst Destroys Ciprofloxacin Antibiotic in Water with Sunlight</title>
		<link>https://scienmag.com/plant-powered-nanocatalyst-destroys-ciprofloxacin-antibiotic-in-water-with-sunlight/</link>
		
		<dc:creator><![CDATA[Bethany Barker]]></dc:creator>
		<pubDate>Sun, 20 Sep 2026 22:31:41 +0000</pubDate>
				<category><![CDATA[Chemistry]]></category>
		<category><![CDATA[advanced wastewater treatment methods]]></category>
		<category><![CDATA[antibiotic pollution]]></category>
		<category><![CDATA[antibiotic removal from water]]></category>
		<category><![CDATA[Capsella bursa-pastoris]]></category>
		<category><![CDATA[ciprofloxacin]]></category>
		<category><![CDATA[ciprofloxacin degradation]]></category>
		<category><![CDATA[environmental impact of pharmaceutical contaminants]]></category>
		<category><![CDATA[green synthesis]]></category>
		<category><![CDATA[magnetic nanocomposites for environmental cleanup]]></category>
		<category><![CDATA[magnetic recovery]]></category>
		<category><![CDATA[MgFe2S4/CoBiO2I heterojunction]]></category>
		<category><![CDATA[mineralization]]></category>
		<category><![CDATA[nanocatalysts for water treatment]]></category>
		<category><![CDATA[nanocomposite]]></category>
		<category><![CDATA[Photocatalysis]]></category>
		<category><![CDATA[plant-based photocatalysts]]></category>
		<category><![CDATA[resistance to antibiotics in water systems]]></category>
		<category><![CDATA[S-scheme mechanism]]></category>
		<category><![CDATA[semiconductor nanomaterials for pollution control]]></category>
		<category><![CDATA[sunlight-driven water purification]]></category>
		<category><![CDATA[sustainable water treatment technologies]]></category>
		<category><![CDATA[visible light]]></category>
		<category><![CDATA[Water pollution]]></category>
		<category><![CDATA[Water treatment]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=203528</guid>

					<description><![CDATA[Researchers used shepherd's purse plant extract to synthesize a magnetic MgFe2S4/CoBiO2I heterojunction photocatalyst that completely degrades the antibiotic ciprofloxacin in water under simulated sunlight.]]></description>
										<content:encoded><![CDATA[<p>Ciprofloxacin, one of the world&#8217;s most widely prescribed fluoroquinolone antibiotics, has become a stubborn fixture of the global water cycle. Detected in surface waters, groundwater and even drinking water supplies at concentrations ranging from nanograms to micrograms per liter, the compound is chemically stable, poorly biodegradable and largely excreted unmetabolized by patients. Conventional wastewater treatment plants, designed to strip out organic matter and nutrients, are largely powerless against it. The consequences are not abstract: trace-level antibiotics are sufficient to select for resistant bacteria, disrupt aquatic microbial communities and inflict genotoxic damage on organisms downstream. Now, a research team led by scientists affiliated with Birjand University of Medical Sciences in Iran reports a plant-based route to a magnetic photocatalyst that can completely eliminate the drug from water under simulated sunlight, offering a greener answer to one of environmental chemistry&#8217;s most persistent problems.</p>
<p>The new material, described in the Journal of the Saudi Chemical Society, is a nanocomposite that marries two semiconductors with complementary talents: magnesium iron sulfide (MgFe2S4), a magnetic spinel sulfide with a narrow band gap, and cobalt bismuth oxyiodide (CoBiO2I), a layered bismuth-based semiconductor that absorbs visible light strongly. Individually, each material falls short. MgFe2S4 nanoparticles tend to aggregate, burying their active sites, and their photogenerated electrons and holes recombine too quickly to do much useful chemistry. CoBiO2I, meanwhile, suffers from photocorrosion, limited surface area and no magnetism at all, making it awkward to recover from treated water. Fused into a single heterostructure, the two phases overcome each other&#8217;s weaknesses, and the resulting core-shell architecture can be pulled out of solution with a simple external magnet.</p>
<p>What sets the study apart is not just the heterojunction but how it was made. Rather than relying on conventional hydrothermal or solvothermal chemistry, which typically demands energy-intensive conditions and toxic reducing agents such as hydrazine or sodium borohydride, the team turned to an extract of Capsella bursa-pastoris, common shepherd&#8217;s purse, collected in South Khorasan Province, Iran. Dried plant powder was extracted with methanol at room temperature over three days, yielding a dark-brown solid rich in flavonoids, tannins, alkaloids and amino acids. These phytochemicals act as biological mediators, reducing metal ions, capping growing nanoparticles and preventing the aggregation that plagues chemically synthesized counterparts. Although methanol extraction and high-temperature calcination at 700 degrees Celsius were still required, the researchers argue the route remains substantially more sustainable than conventional synthesis, and they identify replacing methanol with aqueous extraction and lowering the calcination temperature as priorities for future work.</p>
<p>Characterization confirmed the design worked as intended. X-ray diffraction revealed sharp spinel peaks for MgFe2S4 coexisting with new reflections from CoBiO2I, with no impurity phases, and a Scherrer-analysis crystallite size of roughly 13 nanometers. Infrared spectroscopy showed Mg-S and Fe-S bonds alongside Bi-O-I vibrations, with shifts in the hydroxyl bands hinting at hydrogen bonding across the interface. Field-emission scanning and transmission electron microscopy captured the striking morphology: roughly spherical magnetic cores wrapped in feather-like, interconnected CoBiO2I nanosheets forming a core-shell heterojunction. Energy-dispersive X-ray mapping showed all elements uniformly distributed, with the surface-dominated bismuth signal and weak magnesium and sulfur signals independently confirming the encapsulation of the magnetic core. Vibrating-sample magnetometry recorded saturation magnetization of 27.83 emu per gram for the composite, down from 68.05 for the bare spinel but more than enough for magnetic separation.</p>
<p>Optical measurements explained why the composite outperforms its parents. Diffuse reflectance spectroscopy gave band gaps of about 1.35 electronvolts for MgFe2S4 and 2.39 electronvolts for the composite, a slight blue shift the authors attribute to the formation of an S-scheme heterojunction. In this arrangement, Fermi-level equilibration between the two semiconductors bends their bands and creates an internal electric field that drives low-energy electrons in MgFe2S4 to recombine with low-energy holes in CoBiO2I, while preserving the high-energy electrons and holes that actually drive redox reactions. Photoluminescence spectroscopy provided the corroborating evidence: the composite&#8217;s emission intensity was markedly quenched relative to pure MgFe2S4, indicating sharply suppressed radiative recombination. A conductive carbonaceous residue derived from coke powder used during sulfidation appears to act as an electron shuttle, further extending the lifetime of photogenerated carriers.</p>
<p>Under a 500-watt xenon lamp with a visible-light cutoff, the composite delivered headline results. After optimizing pH, catalyst loading and reaction time, the team achieved complete, 100 percent degradation of ciprofloxacin within 200 minutes at pH 9 with 1 gram per liter of catalyst and an initial drug concentration of 20 milligrams per liter. That represents roughly a 35 percent improvement over the bare magnetic spinel, which managed only 65.29 percent under comparable conditions, while pure CoBiO2I peaked at about 71 percent. Degradation followed pseudo-first-order kinetics, with a rate constant of 0.0349 per minute at the optimized concentration, nearly ten times the 0.0036 per minute measured for MgFe2S4 alone. At lower pollutant concentrations of 5 milligrams per liter, the rate constant rose to 0.0654 per minute, reflecting the concentration dependence typical of surface-mediated photocatalysis.</p>
<p>Importantly, the team did not equate the disappearance of the drug&#8217;s UV-Vis absorption peak with true detoxification. Direct chemical oxygen demand and total organic carbon measurements, taken with a Shimadzu TOC-L analyzer and Hach colorimetric method, showed 79.03 percent COD removal and 54.23 percent TOC removal for the composite, compared with 41.91 and 31.81 percent for MgFe2S4. The gap between degradation and mineralization confirms the formation of intermediate organic compounds, a well-known feature of fluoroquinolone oxidation pathways, and the authors stress that TOC remains the gold-standard metric for judging whether antibiotic treatment genuinely destroys the pollutant rather than merely fragmenting it.</p>
<p>Radical scavenging experiments mapped the reaction mechanism. Adding isopropyl alcohol to trap hydroxyl radicals cut degradation to 53.47 percent, while EDTA, which captures photogenerated holes, reduced it to 61.37 percent, identifying hydroxyl radicals and holes as the dominant reactive species. Chloroform, a superoxide scavenger, lowered efficiency to 87.86 percent and potassium persulfate, an electron scavenger, barely dented it at 98.96 percent, marking electrons and superoxide as minor players. Mott-Schottky analysis placed the conduction band of MgFe2S4 at about minus 0.79 volts versus normal hydrogen electrode, negative enough to reduce oxygen to superoxide, while the valence band of CoBiO2I at 2.64 volts is positive enough to oxidize hydroxide into hydroxyl radicals, exactly the band alignment the S-scheme model predicts.</p>
<p>Practical durability rounded out the case. Across ten consecutive photocatalytic cycles, with the catalyst magnetically recovered, washed and reused each time, the composite retained 87.25 percent of its initial degradation efficiency, a loss the authors attribute to site blockage by by-products, gradual fouling and the wear of repeated washing. Replicate experiments showed a relative percent difference of just 0.30 percent, well within accepted precision thresholds. The authors acknowledge open questions, including whether near-neutral pH, more representative of real wastewater than the optimal alkaline pH 9, can deliver acceptable performance, and they note that direct verification of the S-scheme mechanism through high-resolution interfacial imaging and valence-band XPS was beyond their instrumental reach. They also flag the need to assess long-term metal leaching and the ecotoxicity of degradation intermediates before scale-up. Even so, the combination of complete degradation, strong mineralization, magnetic recyclability and a synthesis route that swaps hydrazine for shepherd&#8217;s purse marks the MgFe2S4/CoBiO2I heterojunction as one of the more compelling entries in the crowded field of visible-light photocatalysts for pharmaceutical pollution.</p>
<p><strong>Subject of Research:</strong> Plant-extract-mediated synthesis of a magnetic MgFe2S4/CoBiO2I heterojunction photocatalyst for degrading the antibiotic ciprofloxacin in water</p>
<p><strong>Article Title:</strong> Phytochemical-mediated design of magnetic MgFe2S4/CoBiO2I heterojunction for enhanced photocatalytic degradation of ciprofloxacin</p>
<p><strong>Article References:</strong> Azqandi, M., Nasseh, N., Esmaeli-Nasrabadi, F., Kargar, M., Ahmadzadeh, S., Dolatabadi, M., &amp; Jahanshahi, R. (2026). Phytochemical-mediated design of magnetic MgFe2S4/CoBiO2I heterojunction for enhanced photocatalytic degradation of ciprofloxacin. <em>Journal of Saudi Chemical Society, 30</em>(5), Article 68. <a href="https://doi.org/10.1007/s44442-026-00118-1" rel="noopener noreferrer">https://doi.org/10.1007/s44442-026-00118-1</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.1007/s44442-026-00118-1" rel="noopener noreferrer">10.1007/s44442-026-00118-1</a></p>
<p><strong>Keywords:</strong> photocatalysis, ciprofloxacin, MgFe2S4/CoBiO2I heterojunction, green synthesis, Capsella bursa-pastoris, antibiotic pollution, water treatment, magnetic recovery, S-scheme mechanism, visible light, mineralization, nanocomposite</p>
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		<post-id xmlns="com-wordpress:feed-additions:1">203528</post-id>	</item>
		<item>
		<title>Polyethylene Microplastics Linger in Soil for Decades as They Quietly Merge With Soil Structure</title>
		<link>https://scienmag.com/polyethylene-microplastics-linger-in-soil-for-decades-as-they-quietly-merge-with-soil-structure/</link>
		
		<dc:creator><![CDATA[Alan Morgan]]></dc:creator>
		<pubDate>Sat, 12 Sep 2026 21:54:28 +0000</pubDate>
				<category><![CDATA[Technology and Engineering]]></category>
		<category><![CDATA[agricultural soils]]></category>
		<category><![CDATA[biodegradation]]></category>
		<category><![CDATA[carbon-13 labeling]]></category>
		<category><![CDATA[effects of microplastics on soil health]]></category>
		<category><![CDATA[environmental fate of microplastics]]></category>
		<category><![CDATA[long-term plastic degradation in soil]]></category>
		<category><![CDATA[microbial degradation of plastics]]></category>
		<category><![CDATA[microplastic carbon isotope tracing]]></category>
		<category><![CDATA[Microplastic soil contamination]]></category>
		<category><![CDATA[microplastics]]></category>
		<category><![CDATA[microplastics in soil]]></category>
		<category><![CDATA[mineralization]]></category>
		<category><![CDATA[nanoplastics]]></category>
		<category><![CDATA[NanoSIMS]]></category>
		<category><![CDATA[plastic degradation]]></category>
		<category><![CDATA[polyethylene]]></category>
		<category><![CDATA[polyethylene microplastics environmental impact]]></category>
		<category><![CDATA[polyethylene microplastics in agriculture]]></category>
		<category><![CDATA[polyethylene persistence in farmland]]></category>
		<category><![CDATA[soil aggregates]]></category>
		<category><![CDATA[soil microplastic integration]]></category>
		<category><![CDATA[soil organic matter]]></category>
		<category><![CDATA[soil pollution]]></category>
		<category><![CDATA[soil structure alteration by microplastics]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=198980</guid>

					<description><![CDATA[A 22-month isotope-labeling experiment shows polyethylene microplastics mineralize at just 0.12 percent in agricultural soil while gradually embedding themselves in soil aggregates and organic matter.]]></description>
										<content:encoded><![CDATA[<p>Polyethylene is everywhere. It wraps our food, lines our agricultural mulch films, and sheds fragments into the ground with every season of use. Now, one of the most detailed long-term experiments ever conducted on plastic in soil has confirmed what many researchers feared: once polyethylene microplastics enter agricultural soil, they barely break down at all — and instead of disappearing, they quietly weave themselves into the very architecture of the soil. A team of German and Swiss researchers, led by Hannah Forsyth and Moritz Bigalke of the Technical University of Darmstadt, incubated isotopically labeled polyethylene in farmland soil for nearly two years and found that just 0.12 percent of the plastic had been converted to carbon dioxide by the end of the experiment.</p>
<p>The study, published in the journal Microplastics and Nanoplastics, stands out for its methodological rigor. Rather than relying on bulk measurements that can be confounded by background carbon, the researchers used polyethylene enriched with carbon-13, a stable isotope that acts as a molecular fingerprint. By tracking the appearance of carbon-13 in carbon dioxide released from the incubated soil, they could measure microbial mineralization with extraordinary precision. Any carbon-13 dioxide detected had to come from the plastic, because natural soil carbon carries a far lower abundance of this heavy isotope. This allowed the team to separate the slow metabolism of plastic-eating microbes from the vast background noise of ordinary soil respiration.</p>
<p>The plastic itself was not simply dropped into the soil as pristine beads. The researchers first aged it with ultraviolet light, mimicking the weathering that plastic undergoes in the field before it is tilled into the ground. UV exposure breaks polymer chains and introduces oxygen-containing chemical groups at the surface, which is widely considered a prerequisite for microbial attack. Even under these favorable conditions, the soil microbial community managed to oxidize only a tiny fraction of the polymer over the 22-month incubation. The mineralization rate was highest early in the experiment and declined over time, suggesting that the most accessible, oxidized surface material was consumed first, leaving behind a polymer core that microbes could barely touch.</p>
<p>Extrapolated to real-world timescales, the numbers are sobering. If 0.12 percent mineralizes in less than two years, and the rate continues to fall as the remaining plastic becomes less accessible, complete degradation of polyethylene in soil would take centuries, if it happens at all under natural conditions. Agricultural soils are among the most plastic-contaminated environments on Earth, receiving fragments from mulch films, plastic-coated fertilizers, irrigation pipes, sewage sludge, and atmospheric deposition. The new findings imply that virtually every gram of polyethylene ever tilled into farmland is still there, either as visible fragments or as microscopic and submicroscopic particles dispersed through the soil matrix.</p>
<p>But persistence is only half of the story. The second major finding concerns where the plastic goes. Using nanoscale secondary ion mass spectrometry, or NanoSIMS, the team mapped the location of the labeled plastic inside individual soil aggregates — the small, crumb-like clusters of mineral particles and organic matter that give soil its structure. They found microplastics and even nanoplastics lodged inside pores within 1-to-2-millimeter aggregates, spaces that are typically sheltered from water flow and physical disturbance. This means plastic particles are not merely sitting on the soil surface; they are being transported into the interior architecture of aggregates, where they can reside for very long periods and become increasingly difficult to extract or study.</p>
<p>The physical integration of plastic into soil structure has consequences that go beyond simple contamination. Soil aggregates regulate water infiltration, aeration, root penetration, and the protection of organic carbon from decomposition. Introducing hydrophobic polymer surfaces into these delicate structures can alter how water and gases move through the soil, and may change how aggregates form and break apart. The study also found small but measurable amounts of polyethylene-derived carbon-13 incorporated into soil organic matter and into the microbial biomass itself. This indicates that some carbon from the plastic does enter the soil&#8217;s biological and chemical cycles — not through rapid mineralization, but through slow assimilation into the organic pool that sustains soil fertility.</p>
<p>That incorporation, however, was minor. The overwhelming majority of the labeled carbon remained as intact or partially oxidized polymer. For the researchers, this combination of extreme persistence and gradual integration is the key takeaway. Polyethylene does not vanish in soil; it becomes part of the soil. Over years and decades, fragments fragment further, migrate into smaller pores, associate with mineral surfaces and organic matter, and effectively become a permanent, synthetic component of the terrestrial environment. Unlike organic amendments that decompose into nutrients, this material accumulates, and its long-term effects on soil health remain largely unknown.</p>
<p>The work was carried out under the MINAGRIS project — MIcro- and Nanoplastics in AGRIcultural Soils — funded by the European Union&#8217;s Horizon 2020 research and innovation program. The project brings together institutions across Europe to assess how plastic debris affects soil biodiversity, productivity, and function. The new results provide a quantitative foundation for those assessments, offering hard numbers on mineralization rates that can feed into models of plastic accumulation in farmland. They also validate the use of isotope labeling combined with high-resolution imaging as a powerful toolkit for studying the fate of plastics in complex environmental matrices, where traditional extraction methods miss particles embedded deep within aggregates.</p>
<p>For farmers and policymakers, the message is clear: prevention matters far more than remediation. No known technology can remove microplastics from soil once they are incorporated, and the new data suggest there will be ample time for them to spread. Reducing plastic inputs to agricultural land — through biodegradable mulch alternatives, better recovery of plastic films, restrictions on sewage-sludge application, and improved waste management — is currently the only effective strategy for limiting the buildup. As the researchers demonstrate, every year of continued plastic input adds material that will remain in the ground long after current farming practices have changed.</p>
<p>The study also raises questions for future research. The incubation captured a single soil type under controlled laboratory conditions; field soils experience freeze-thaw cycles, wetting-drying pulses, root growth, and tillage, all of which can physically fragment plastic and redistribute it. Whether these processes accelerate mineralization or simply enhance the physical dispersion of particles into aggregates is an open question. What is already certain, however, is that polyethylene&#8217;s reputation as an inert, harmless filler material in soil is untenable. It persists, it infiltrates, and it slowly becomes one with the ground beneath our feet — a legacy that future generations of soil scientists, and farmers, will have to live with.</p>
<p><strong>Subject of Research:</strong> Fate, mineralization, and physical integration of polyethylene microplastics in agricultural soil</p>
<p><strong>Article Title:</strong> Polyethylene microplastics mineralize slowly in soil but integrate into soil structures and organic matter</p>
<p><strong>Article References:</strong> Forsyth, H., Schweizer, S., Stricker, K., Höschen, C., Velescu, A., Wilcke, W., &amp; Bigalke, M. (2026). Polyethylene microplastics mineralize slowly in soil but integrate into soil structures and organic matter. <em>Microplastics and Nanoplastics, 6</em>(1), Article 54. <a href="https://doi.org/10.1186/s43591-026-00223-3" rel="noopener noreferrer">https://doi.org/10.1186/s43591-026-00223-3</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.1186/s43591-026-00223-3" rel="noopener noreferrer">10.1186/s43591-026-00223-3</a></p>
<p><strong>Keywords:</strong> polyethylene, microplastics, nanoplastics, soil pollution, mineralization, carbon-13 labeling, soil aggregates, soil organic matter, biodegradation, agricultural soils, NanoSIMS, plastic degradation</p>
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		<post-id xmlns="com-wordpress:feed-additions:1">198980</post-id>	</item>
		<item>
		<title>Ozone, UV Light and Hydrogen Peroxide Team Up to Destroy Wastewater Drug Residue</title>
		<link>https://scienmag.com/ozone-uv-light-and-hydrogen-peroxide-team-up-to-destroy-wastewater-drug-residue/</link>
		
		<dc:creator><![CDATA[Sloane Callahan]]></dc:creator>
		<pubDate>Sat, 12 Sep 2026 19:53:29 +0000</pubDate>
				<category><![CDATA[Climate]]></category>
		<category><![CDATA[acetaminophen]]></category>
		<category><![CDATA[advanced oxidation processes]]></category>
		<category><![CDATA[advanced oxidation processes for drug residue]]></category>
		<category><![CDATA[chemical oxygen demand]]></category>
		<category><![CDATA[combined oxidant and light treatment for water safety]]></category>
		<category><![CDATA[degradation of acetaminophen in sewage]]></category>
		<category><![CDATA[energy-efficient wastewater treatment methods]]></category>
		<category><![CDATA[environmental impact of over-the-counter medicines]]></category>
		<category><![CDATA[global drug pollution in water systems]]></category>
		<category><![CDATA[hydrogen peroxide]]></category>
		<category><![CDATA[hydrogen peroxide in water pollution cleanup]]></category>
		<category><![CDATA[hydroxyl radicals]]></category>
		<category><![CDATA[innovative solutions for persistent water pollutants]]></category>
		<category><![CDATA[innovative water purification technologies]]></category>
		<category><![CDATA[mineralization]]></category>
		<category><![CDATA[ozone]]></category>
		<category><![CDATA[Ozone-based wastewater treatment]]></category>
		<category><![CDATA[paracetamol]]></category>
		<category><![CDATA[pharmaceutical pollution]]></category>
		<category><![CDATA[removal of pharmaceutical contaminants from surface water]]></category>
		<category><![CDATA[ultraviolet radiation]]></category>
		<category><![CDATA[UV light oxidation for pharmaceutical removal]]></category>
		<category><![CDATA[wastewater treatment]]></category>
		<category><![CDATA[water purification]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=198100</guid>

					<description><![CDATA[A new study shows that combining ozone, hydrogen peroxide, and ultraviolet radiation degrades up to 99 percent of acetaminophen in water within an hour, with lower energy demand and reduced toxicity than most individual treatments.]]></description>
										<content:encoded><![CDATA[<p>One of the world&#8217;s most widely consumed medicines has become one of the world&#8217;s most stubborn water pollutants, and a new study suggests that a carefully choreographed trio of oxidants and light can dismantle it almost completely. Acetaminophen, known as paracetamol in much of the world, is ingested at an estimated 145,000 tonnes per year, and whatever the body does not metabolize is excreted into sewage systems. Conventional wastewater treatment plants are poorly equipped to break it down, and researchers have now demonstrated that combining hydrogen peroxide, ozone, and ultraviolet radiation degrades up to 99 percent of the drug in just one hour, while consuming less energy per unit of pollutant removed than many competing technologies.</p>
<p>The research, published in Cleaner Engineering and Technology by a team from the Tecnológico Nacional de México led by Bethsabet Jaramillo-Sierra, tackles a contamination problem that spans the globe. Acetaminophen has been detected in wastewater and surface waters on nearly every continent, at concentrations ranging from tens of nanograms per liter in France and Canada to hundreds of micrograms per liter in Colombia and northern Mexico. Although each individual measurement may seem small, the compound&#8217;s sheer consumption volume, its availability over the counter, and its resistance to biological degradation mean it accumulates persistently in rivers, drinking water sources, and even treated effluents.</p>
<p>The concern is not merely the presence of the parent molecule. Acetaminophen is poorly biodegradable, so it passes through conventional treatment largely intact, and it has been linked in laboratory studies to genetic damage, oxidative lipid degradation, and liver injury in living organisms. Worse still, during some tertiary treatment steps the compound can transform into by-products that are more dangerous than the original drug, including 1,4-benzoquinone and N-acetyl-p-benzoquinone imine, a hepatotoxic metabolite capable of causing hepatic failure and necrosis. Any credible remediation strategy must therefore do more than hide the molecule; it must destroy it or convert it into harmless end products.</p>
<p>The Mexican team turned to advanced oxidation processes, or AOPs, a family of water treatment methods that operate at ambient temperature and pressure and rely on the generation of highly reactive chemical species, most notably the hydroxyl radical. This radical carries a higher oxidation potential than chlorine and reacts non-selectively with a broad range of organic pollutants, which makes it attractive for treating trace contaminants of many kinds. AOPs also avoid sludge production, do not require adsorbents that need controlled disposal, and can be driven by easily handled reagents such as ozone and hydrogen peroxide, with ozone generated on site from atmospheric air to reduce storage and transport costs.</p>
<p>The experimental apparatus was deliberately simple: a cylindrical stainless-steel reactor with an 11-watt ultraviolet lamp emitting at 200 to 280 nanometers, housed in a quartz tube, coupled to a 12-watt ozone generator and a recirculating reservoir. Synthetic solutions of acetaminophen at 100 milligrams per liter were treated for 60 minutes in 500-milliliter batches, with hydrogen peroxide added at doses of 5, 10, and 15 milligrams per liter. Degradation was tracked by ultraviolet-visible spectrophotometry, chemical oxygen demand was measured colorimetrically, and oxidation by-products were identified using gas chromatography-mass spectrometry following solid-phase extraction.</p>
<p>The results revealed a clear hierarchy of effectiveness. Ultraviolet light alone managed only about 11 percent degradation in an hour, primarily by photolyzing water molecules into hydroxyl radicals and hydrogen atoms, a process that accelerates around the 254-nanometer wavelength. Hydrogen peroxide alone reached roughly 27 percent at the highest dose. Ozone alone, attacking through both direct molecular oxidation and indirect decomposition into hydroxyl radicals, achieved 73 percent. Pairing ozone with ultraviolet light pushed the figure to 84 percent, because photolysis of dissolved ozone generates additional atomic oxygen, hydroxyl radicals, and even hydrogen peroxide in solution, creating multiple parallel destruction pathways.</p>
<p>The real breakthrough came when all three agents were applied simultaneously. The ozone-hydrogen peroxide combination, known as peroxone, promotes hydroxyl radical formation through the mutual reaction of the two oxidants, and adding ultraviolet irradiation on top of this triggered photolysis of both peroxide and dissolved ozone. Under these conditions, with an initial hydrogen peroxide concentration of just 5 milligrams per liter, the team achieved 99 percent acetaminophen degradation in 60 minutes. Notably, the study found an optimal peroxide dose: higher concentrations of 10 and 15 milligrams per liter actually performed worse over time, because excess peroxide and the hydroperoxyl radical it forms act as scavengers, consuming the very hydroxyl radicals that destroy the pollutant.</p>
<p>Chemical analysis confirmed that the combined treatment went beyond mere transformation. Carbon dioxide production rose steadily across the treatment combinations, peaking at 37 milligrams per liter for the triple system, evidence of genuine mineralization rather than simple conversion to other organics. Chemical oxygen demand removal reached 74 percent in the same configuration, compared with just 9 percent for ultraviolet light alone. Color measurements told a parallel story: untreated solutions stayed clear, ultraviolet treatment alone produced a pale carmine tint at 150 platinum-cobalt units as aromatic ring breakdown products accumulated, while the triple system yielded only a faint yellow at 5 units, indicating that even the colored intermediates were being further oxidized. Gas chromatography-mass spectrometry identified by-products dominated by carboxylic acid, ester, and alcohol structures arising from aromatic ring cleavage and recombination, and crucially, the team did not detect hydroquinone or 1,4-benzoquinone, suggesting these hazardous intermediates were themselves degraded during the process.</p>
<p>Energetically, the triple treatment also proved competitive. The researchers calculated the electrical energy per order, a standard metric describing the kilowatt-hours needed to reduce pollutant concentration by one order of magnitude per cubic meter, and obtained 23.00 kilowatt-hours per cubic meter for the peroxide-ozone-UV system, well below the 537 kilowatt-hours per cubic meter required for ultraviolet treatment alone and below several values reported in comparable literature. The estimated operating cost of the best configuration came to 5.04 US dollars per cubic meter, with ultraviolet irradiation dominating the energy bill, ozone generation second, and hydrogen peroxide contributing least. The degradation kinetics followed a pseudo first-order model, with rate constants rising as processes were combined, consistent with the theory that degradation depends primarily on pollutant concentration while oxidant doses remain effectively constant.</p>
<p>Finally, the team assessed whether the treated water was actually safer, using the germination of lettuce seeds as a biological toxicity screen. Untreated and lightly treated samples showed moderate toxicity, with ozone alone inhibiting germination by 40 percent, a sign that oxidative intermediates can be more harmful than the parent drug. But the full triple treatment reduced inhibition to 15 percent, close to the control level, demonstrating that synergistic oxidation both destroys the pollutant and neutralizes its residual toxic footprint. Taken together, the findings position the combined peroxide-ozone-UV process as an operationally simple, reproducible, and relatively inexpensive route to eliminating one of the world&#8217;s most ubiquitous pharmaceutical pollutants, though the authors note that complete mineralization would likely require longer treatment times or more intensified oxidative conditions to drive the remaining low-complexity organic by-products all the way to inorganic carbon.</p>
<p><strong>Subject of Research:</strong> Degradation of the pharmaceutical pollutant acetaminophen in water using combined advanced oxidation processes involving ozone, hydrogen peroxide, and ultraviolet radiation.</p>
<p><strong>Article Title:</strong> Acetaminophen degradation process applying a combination of oxidizing agents and ultraviolet radiation</p>
<p><strong>Article References:</strong> Jaramillo-Sierra, B., Mercado-Cabrera, A., Ibañez-Olvera, M., Peña-Eguíluz, R., Rodríguez-Méndez, B. G., &amp; López-Callejas, R. (2026). Acetaminophen degradation process applying a combination of oxidizing agents and ultraviolet radiation. <em>Cleaner Engineering and Technology, 34</em>, Article 101301. <a href="https://doi.org/10.1016/j.clet.2026.101301" rel="noopener noreferrer">https://doi.org/10.1016/j.clet.2026.101301</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.1016/j.clet.2026.101301" rel="noopener noreferrer">10.1016/j.clet.2026.101301</a></p>
<p><strong>Keywords:</strong> acetaminophen, paracetamol, advanced oxidation processes, ozone, hydrogen peroxide, ultraviolet radiation, hydroxyl radicals, wastewater treatment, pharmaceutical pollution, water purification, mineralization, chemical oxygen demand</p>
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		<post-id xmlns="com-wordpress:feed-additions:1">198100</post-id>	</item>
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