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	<title>soil aggregates &#8211; Science</title>
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	<title>soil aggregates &#8211; Science</title>
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		<title>Biodegradable Plastic Mulch Residues Reshape Soil Life Differently in Loamy and Sandy Soils</title>
		<link>https://scienmag.com/biodegradable-plastic-mulch-residues-reshape-soil-life-differently-in-loamy-and-sandy-soils/</link>
		
		<dc:creator><![CDATA[Alan Morgan]]></dc:creator>
		<pubDate>Fri, 16 Oct 2026 05:26:31 +0000</pubDate>
				<category><![CDATA[Earth Science]]></category>
		<category><![CDATA[Science News]]></category>
		<category><![CDATA[biodegradable plastic mulch]]></category>
		<category><![CDATA[carbon sequestration]]></category>
		<category><![CDATA[Mater-Bi]]></category>
		<category><![CDATA[microbial biomass carbon]]></category>
		<category><![CDATA[microplastics]]></category>
		<category><![CDATA[nitrogen cycling]]></category>
		<category><![CDATA[qPCR]]></category>
		<category><![CDATA[soil aggregates]]></category>
		<category><![CDATA[soil biogeochemistry]]></category>
		<category><![CDATA[soil organic carbon]]></category>
		<category><![CDATA[soil texture]]></category>
		<category><![CDATA[stable isotopes]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=282082</guid>

					<description><![CDATA[A year-long incubation study shows that biodegradable plastic mulch residues stimulate microbial biomass and reshape soil aggregates differently in loamy and sandy soils, with effects strongly dependent on dose and texture.]]></description>
										<content:encoded><![CDATA[<p>Biodegradable plastic mulches have been heralded as a greener alternative to the conventional polyethylene films that blanket vegetable fields around the world. Unlike traditional plastic, which must be painstakingly peeled off the soil at the end of each season and often ends up fragmenting into persistent microplastics, soil-biodegradable plastics are designed to be tilled straight into the ground, where microbes should eventually dismantle them. But that promise comes with a hidden twist: as these films break down, they release an entirely new source of carbon into the soil, and nobody fully understands what that influx does to the invisible ecosystems and physical architecture beneath our feet. A new year-long laboratory study from the University of Bologna, published in Frontiers in Soil Science, now offers one of the most detailed pictures yet, and its central finding is striking: the same biodegradable plastic can leave two very different fingerprints depending on whether it lands in a loamy or a sandy soil.</p>
<p>The research team, led by Paola Gioacchini and Martina Mazzon, took two contrasting agricultural soils, a loamy Cambisol rich in silt and clay and a sandy Arenosol dominated by coarse particles, and mixed in fragments of a commercial biodegradable mulch film made of Mater-Bi, a starch-based polymer produced by Novamont. The fragments, sized between two and five millimeters, were added at three concentrations: 100, 1,000 and 10,000 milligrams per kilogram of dry soil, corresponding to 0.01, 0.1 and 1 percent by weight. The lowest dose mirrors the estimated annual input of biodegradable mulch material in a realistic agronomic setting, while the highest matches the loading rate recommended by the European standard EN 17033 for testing biodegradability. The soils were then incubated at 23 degrees Celsius, held at 60 percent of their water-holding capacity, for a full twelve months, with microbial measurements taken at the start, at six months and at the end of the experiment.</p>
<p>The clearest signal emerged at the highest dose, and it was dramatic. After one year, microbial biomass carbon, a measure of the living microbial community, was 69 percent higher in the loamy soil and 25 percent higher in the sandy soil compared with untreated controls. Because the biodegradable plastic contains roughly 60 percent carbon and no nitrogen, the highest dose delivered a hefty 6,000 milligrams of carbon per kilogram of soil, essentially a feast for soil microbes. At the six-month mark, the effect was already visible, with microbial biomass reaching approximately 583 milligrams per kilogram in the loamy soil and 238 in the sandy soil. Even though microbial biomass declined in all treatments between six and twelve months, the highest-dose treatment remained significantly elevated above both the control and the lower doses, suggesting that a large pulse of plastic-derived carbon can sustain microbial growth for a remarkably long time.</p>
<p>Quantitative PCR of bacterial 16S rRNA genes and fungal target genes revealed a more nuanced, and partly surprising, story. In the sandy soil, the intermediate dose of 1,000 milligrams per kilogram produced the highest bacterial and fungal gene abundance across the two sampling times, outperforming even the highest dose. The researchers suspect this counterintuitive result relates to carbon losses measured in a companion study: at the highest dose, the sandy soil had released extremely large amounts of carbon dioxide early in the incubation, meaning much of the available carbon may have escaped as gas rather than being converted into microbial cells. In the loamy soil, by contrast, microbial responses were strongly time-dependent, with the highest dose producing peak fungal abundance at six months. The prominence of fungi fits with earlier work showing that fungi are key colonizers and degraders of biodegradable plastics, thanks in part to their ability to produce cutinases, enzymes that accelerate polymer breakdown and carbon release.</p>
<p>Beyond the microbes, the plastic fragments physically restructured both soils. At the end of the year, the researchers used wet sieving to separate each soil into three size classes: macroaggregates larger than 250 micrometers, microaggregates between 250 and 50 micrometers, and the free silt-clay fraction below 50 micrometers. The highest plastic dose increased macroaggregate abundance by 32 percent in the loamy soil and 11 percent in the sandy soil, while sharply reducing the free silt-clay fraction, which fell to just 8.9 percent of the loamy soil&#8217;s mass compared with 28.5 percent in the untreated control. The likely mechanism is twofold: the plastic fragments can act as nuclei around which mineral particles, microbial biomass and organic matter coalesce into larger aggregates, and the surge in microbial growth supplies the sticky residues and extracellular substances that bind those particles together.</p>
<p>Crucially, the researchers corrected aggregate weights for sand content, since the sandy soil&#8217;s aggregates were up to 90 percent sand by weight, allowing a fair comparison between the two textures. This revealed that the loamy soil inherently holds far more real aggregate material, with 78 percent more macroaggregates and 71 percent more microaggregates than the sandy soil. The lower plastic doses produced weaker and more soil-specific effects: in the loamy soil, the two lower doses increased the recovery of microaggregates to about 50 percent of the soil mass, possibly because macroaggregates formed early in the incubation broke down and freed microaggregates previously locked inside them. In the sandy soil, only the highest dose shifted aggregate composition at all, underscoring how coarse-textured soils resist structural change unless the input is large.</p>
<p>The redistribution of aggregates carried carbon and nitrogen with it. The highest plastic dose increased carbon and nitrogen contents in macroaggregates in both soils, and also in the sandy soil&#8217;s microaggregates, while the free silt-clay fraction lost both elements. According to the classic aggregate-turnover model of Six and colleagues, this occlusion of fine particles within macroaggregates may actually protect carbon and nitrogen from microbial attack and mineralization, since physical barriers inside aggregates limit oxygen diffusion and enzyme access. The carbon-to-nitrogen ratio narrowed steadily from macroaggregates down to the silt-clay fraction in both soils, a signature of the predominantly microbial origin of organic matter in the finest fractions, where nitrogen-rich microbial residues accumulate and bind chemically to mineral surfaces.</p>
<p>Stable isotopes added a final layer of insight, and an unexpected one. Nitrogen isotope values, expressed as δ15N, rose progressively from macroaggregates to the finest fractions in both soils, indicating extensive microbial recycling of nitrogen in the smaller fractions, although the plastic itself had no effect on this pattern in the loamy soil and only a modest one in the sandy soil. Carbon isotopes told a different story in each soil: in the loamy soil, the silt-clay fraction was enriched in carbon-13, consistent with repeated microbial processing leaving heavier isotopes behind, while in the sandy soil the finest fraction was actually depleted in carbon-13, possibly reflecting rapid mineralization in which microbes preferentially consumed the lighter, labile compounds and left recalcitrant, carbon-13-depleted molecules stabilized on mineral surfaces. These isotopic shifts were driven by soil texture rather than by the plastic, showing that the soil itself, not the added carbon, governs the pathways of transformation and stabilization.</p>
<p>The authors are careful to note the caveats. The strongest responses occurred at 1 percent plastic by weight, an order of magnitude above realistic annual inputs, and the closed incubation system prevented nitrate leaching, which may have masked some nitrogen isotope effects. Yet the fact that even the lowest, field-realistic dose produced detectable changes in microaggregate recovery and associated carbon and nitrogen is a warning worth heeding. As biodegradable mulches are tilled into fields season after season, their residues will accumulate, and whether the effects documented here persist, amplify or fade over years of repeated incorporation remains an open question. The researchers argue that long-term field studies with repeated applications, focused on realistic doses, are now essential before the soil-biodegradable plastic revolution can be declared truly benign for the ground it is meant to protect.</p>
<p><strong>Subject of Research:</strong> Effects of biodegradable plastic mulch residues on soil microbial biomass, aggregation, and carbon and nitrogen stabilization in loamy and sandy soils</p>
<p><strong>Article Title:</strong> Contrasting responses of loamy and sandy soils to biodegradable plastic residues: microbial biomass, aggregation, and aggregate-associated carbon and nitrogen</p>
<p><strong>Article References:</strong> Contrasting responses of loamy and sandy soils to biodegradable plastic residues: microbial biomass, aggregation, and aggregate-associated carbon and nitrogen. (n.d.). <a href="https://doi.org/10.3389/fsoil.2026.1950823" rel="noopener noreferrer">https://doi.org/10.3389/fsoil.2026.1950823</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.3389/fsoil.2026.1950823" rel="noopener noreferrer">10.3389/fsoil.2026.1950823</a></p>
<p><strong>Keywords:</strong> biodegradable plastic mulch, soil aggregates, microbial biomass carbon, soil organic carbon, nitrogen cycling, stable isotopes, soil texture, microplastics, soil biogeochemistry, Mater-Bi, qPCR, carbon sequestration</p>
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		<post-id xmlns="com-wordpress:feed-additions:1">282082</post-id>	</item>
		<item>
		<title>Straw or Biochar? Scientists Uncover Two Distinct Routes to Carbon-Rich Saline Soils</title>
		<link>https://scienmag.com/straw-or-biochar-scientists-uncover-two-distinct-routes-to-carbon-rich-saline-soils/</link>
		
		<dc:creator><![CDATA[Alan Morgan]]></dc:creator>
		<pubDate>Thu, 15 Oct 2026 00:18:06 +0000</pubDate>
				<category><![CDATA[Agriculture]]></category>
		<category><![CDATA[Biochar]]></category>
		<category><![CDATA[biochar application in coastal farmland]]></category>
		<category><![CDATA[biochar vs straw for carbon storage]]></category>
		<category><![CDATA[carbon sequestration]]></category>
		<category><![CDATA[carbon-rich saline soil recovery]]></category>
		<category><![CDATA[Climate Mitigation]]></category>
		<category><![CDATA[effects of crop straw on soil health]]></category>
		<category><![CDATA[impact of salinity on microbial communities]]></category>
		<category><![CDATA[long-term effects of organic amendments on soil carbon]]></category>
		<category><![CDATA[manure]]></category>
		<category><![CDATA[microbial necromass]]></category>
		<category><![CDATA[organic amendments in saline soils]]></category>
		<category><![CDATA[organic matter stabilization mechanisms]]></category>
		<category><![CDATA[saline soils]]></category>
		<category><![CDATA[saline soils remediation]]></category>
		<category><![CDATA[soil aggregates]]></category>
		<category><![CDATA[soil carbon sequestration]]></category>
		<category><![CDATA[soil health]]></category>
		<category><![CDATA[soil improvement techniques for salt-affected lands]]></category>
		<category><![CDATA[soil microbiome]]></category>
		<category><![CDATA[soil organic carbon]]></category>
		<category><![CDATA[straw]]></category>
		<category><![CDATA[sustainable agriculture in high salinity areas]]></category>
		<category><![CDATA[Yellow River Delta]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=272419</guid>

					<description><![CDATA[A two-year field experiment in China's Yellow River Delta shows that straw and biochar both raise soil organic carbon in saline farmland by about 19 percent, but straw works through microbial transformation while biochar works through physical protection.]]></description>
										<content:encoded><![CDATA[<p>Soils hold more carbon than the atmosphere and all vegetation combined, which makes every insight into how farmland locks away organic matter a matter of global consequence. Yet one of the most widespread obstacles to that storage is rarely headline news: salinity. In salt-affected coastal plains, high salt concentrations suppress plant growth, starve the soil of organic inputs, and weaken the microbial communities that convert plant residues into stable soil organic carbon. A new two-year field experiment in China&#8217;s Yellow River Delta, published in the journal Biochar by researchers from the Chinese Academy of Agricultural Sciences and collaborating institutions, now shows that two of the most popular organic amendments in agriculture, crop straw and biochar, both boost carbon storage in these degraded soils, but they do so through fundamentally different mechanisms.</p>
<p>The study compared four fertilizer treatments over two growing seasons: conventional chemical fertilizer, manure supplementation, and manure combined with either straw or biochar. The setting was deliberately challenging. The Yellow River Delta is characterized by high soil salinity and chronically low organic matter, conditions that limit agricultural productivity across vast areas of coastal farmland. Rather than measuring only how much carbon accumulated at the end of the experiment, the team dissected the process itself, tracking soil organic carbon, microbial community composition, enzyme activities, and the three-dimensional pore structure of the soil. That combination of chemical, biological, and physical measurements is what allowed the researchers to see that the two amendments were not simply adding carbon in parallel; they were reshaping the soil in entirely different ways.</p>
<p>The headline result is deceptively simple. In 2023, both the straw-plus-manure and biochar-plus-manure treatments increased soil organic carbon by approximately 19 percent compared with manure alone. For farmers and policymakers, that means either material can meaningfully improve carbon stocks in salt-affected soils. But the researchers&#8217; deeper analysis revealed that the similarity ends at the number. Straw, it turns out, works primarily through biology, while biochar works primarily through physics. Understanding that distinction, the authors argue, is essential for designing soil management strategies that genuinely improve fertility and support carbon sequestration rather than merely inflating short-term carbon readings.</p>
<p>When straw was mixed with manure, it supplied a flood of readily available organic compounds that stimulated the soil&#8217;s microbial residents. Fed by this fresh substrate, microorganisms ramped up their production of carbon-cycling enzymes, accelerating the decomposition and transformation of organic matter. Crucially, this heightened activity promoted the accumulation of microbial necromass, the chemically stable remains of dead microorganisms that are increasingly recognized as a major, persistent component of soil organic matter. Compared with manure alone, the straw treatment increased total microbial necromass carbon by 10.8 percent and fungal necromass carbon by 11.2 percent. In other words, straw does not simply sit in the soil as carbon; it passes through living organisms, and much of what they leave behind becomes long-lasting soil carbon.</p>
<p>Biochar took the opposite route. Rather than primarily fueling microbial carbon transformation, the charcoal-like material, produced by heating biomass in low-oxygen conditions, acted on the soil&#8217;s architecture. The biochar treatment increased the proportion of large soil aggregates by 40.9 percent and improved aggregate stability by 31.9 percent relative to manure alone. Aggregates are the clumps of mineral particles and organic matter that give healthy soils their crumbly structure, and they matter enormously for carbon storage because organic material sealed inside stable aggregates is physically shielded from decomposers. Biochar also increased soil porosity, creating a more favorable physical environment in which carbon can be retained rather than rapidly mineralized and lost to the atmosphere as carbon dioxide.</p>
<p>Microbial community analyses added a further layer of nuance to the two pathways. The straw treatment reduced the abundance of certain microbial groups dominated by Actinobacteria, a phylum of bacteria often associated with the breakdown of complex organic compounds. Biochar, by contrast, promoted fungal groups dominated by Ascomycota, and those fungal populations were positively associated with soil carbon storage. This shift toward fungi is consistent with the physical-protection story: fungal hyphae physically bind soil particles into aggregates, so a fungal-dominated community can reinforce the very structures that biochar helps create. The two amendments, in effect, cultivate different biological neighborhoods that reinforce their respective carbon-storing strategies.</p>
<p>Taken together, the findings describe two complementary routes to carbon sequestration in degraded farmland. Straw drives biological transformation, converting fresh plant carbon into microbial residues that persist in the soil. Biochar drives physical protection, building the aggregate and pore structures that shelter organic carbon from decomposition. Neither pathway is inherently superior, and the study suggests that the choice between them, or the decision to use both, should depend on management goals. A farmer prioritizing rapid nutrient cycling and fertility building may favor straw, while one focused on long-term structural restoration of compacted or degraded soil may find biochar more effective. Combining the biological and physical mechanisms could, in principle, offer the benefits of both.</p>
<p>The research also carries a broader lesson about how carbon sequestration in agriculture should be evaluated. As corresponding author Hongyuan Zhang put it, selecting organic amendments should involve more than measuring how much carbon they add to soil; understanding how carbon is processed and protected can help guide more effective restoration of degraded agricultural land. That distinction matters because carbon that is merely added to soil can be lost again within months, whereas carbon that has been transformed into microbial necromass or locked inside stable aggregates is far more likely to persist. Carbon accounting schemes and climate mitigation programs that reward farmers for soil carbon gains could produce very different outcomes depending on whether the carbon they measure is biologically stabilized, physically protected, or simply sitting loose in the profile.</p>
<p>The implications extend well beyond the Yellow River Delta. Salt-affected soils occupy substantial areas of global farmland, and land degradation continues to erode the carbon storage capacity of agricultural systems worldwide. Improving carbon inputs and stabilization in these marginal lands offers a rare dual benefit: restoring soil health and productivity for the people who farm them while removing carbon dioxide from the atmosphere. The study&#8217;s demonstration that amendment choice shapes the mechanism of sequestration gives land managers a practical lever, allowing strategies to be matched to local conditions such as soil texture, salinity level, and the availability of crop residues or biochar feedstock.</p>
<p>The researchers are careful to note that longer-term field observations are needed to determine how these mechanisms influence carbon persistence over time. A two-year experiment can reveal pathways, but soil carbon dynamics unfold over decades, and the durability of straw-derived microbial necromass or biochar-stabilized aggregates under continued salinity stress remains an open question. Still, the study provides a clear and actionable framework: in salt-affected soils, carbon storage is not a single process but a contest between biological transformation and physical protection, and the amendments farmers choose determine which of those levers gets pulled. As agriculture faces simultaneous pressures to feed a growing population and stabilize the climate, that kind of mechanistic clarity may prove as valuable as the carbon itself.</p>
<p><strong>Subject of Research:</strong> Divergent mechanisms of straw versus biochar amendment for soil organic carbon sequestration in coastal saline soils</p>
<p><strong>Article Title:</strong> Two paths to healthier soils: Scientists reveal how straw and biochar store carbon differently</p>
<p><strong>Article References:</strong> Two paths to healthier soils: Scientists reveal how straw and biochar store carbon differently. (n.d.). <a href="https://www.eurekalert.org/news-releases/1147789" 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> soil organic carbon, biochar, straw, saline soils, carbon sequestration, microbial necromass, soil aggregates, Yellow River Delta, soil health, manure, climate mitigation, soil microbiome</p>
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		<post-id xmlns="com-wordpress:feed-additions:1">272419</post-id>	</item>
		<item>
		<title>Manure Beats Commercial Organic Fertilizer in Drought-Hit Wheat Fields</title>
		<link>https://scienmag.com/manure-beats-commercial-organic-fertilizer-in-drought-hit-wheat-fields/</link>
		
		<dc:creator><![CDATA[Alan Morgan]]></dc:creator>
		<pubDate>Tue, 13 Oct 2026 12:49:40 +0000</pubDate>
				<category><![CDATA[Agriculture]]></category>
		<category><![CDATA[advantages of pig manure in semi-arid climates]]></category>
		<category><![CDATA[comparison of chemical and organic fertilizers in water-scarce agriculture]]></category>
		<category><![CDATA[coupling coordination]]></category>
		<category><![CDATA[drought resilience]]></category>
		<category><![CDATA[dryland agriculture]]></category>
		<category><![CDATA[effects of organic amendments on crop performance during drought]]></category>
		<category><![CDATA[impact of nitrogen source substitution on wheat yield]]></category>
		<category><![CDATA[influence of organic nutrient sources on crop productivity]]></category>
		<category><![CDATA[Loess Plateau]]></category>
		<category><![CDATA[long-term field experiment on rainfed winter wheat]]></category>
		<category><![CDATA[manure substitution]]></category>
		<category><![CDATA[nitrogen management]]></category>
		<category><![CDATA[nitrogen management in rainfed wheat farming]]></category>
		<category><![CDATA[Organic fertilizer]]></category>
		<category><![CDATA[Organic manure versus commercial organic fertilizer in drought-affected wheat cultivation]]></category>
		<category><![CDATA[rainfed farming]]></category>
		<category><![CDATA[role of pig manure in enhancing wheat resilience]]></category>
		<category><![CDATA[soil aggregates]]></category>
		<category><![CDATA[soil quality index]]></category>
		<category><![CDATA[sustainable fertilization practices in drought-prone regions]]></category>
		<category><![CDATA[water-use efficiency]]></category>
		<category><![CDATA[winter wheat]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=267839</guid>

					<description><![CDATA[A four-year field trial on China's Loess Plateau shows that replacing a quarter of chemical nitrogen with pig manure outperforms commercial organic fertilizer in yield, soil quality, and drought resilience for rainfed winter wheat.]]></description>
										<content:encoded><![CDATA[<p>On the wind-scoured Loess Plateau of northern China, where rainfed winter wheat survives on whatever precipitation falls between autumn sowing and summer harvest, a long-running field experiment has delivered a deceptively simple verdict with far-reaching consequences: not all organic fertilizers are created equal. A team of researchers led by Yanrong Lin and Xiaoli Chen of Northwest A&amp;F University reports in the Journal of Agriculture and Food Research that, under identical total nitrogen inputs, substituting a quarter of chemical fertilizer nitrogen with pig manure outperformed both pure chemical fertilization and substitution with commercial organic fertilizer across four consecutive growing seasons. The advantage was most dramatic in drought years, precisely where rainfed agriculture is most fragile.</p>
<p>The experiment, established in 2017 at the Heyang Wheat-Maize Experimental Station in Shaanxi Province, sits in a warm-temperate semiarid monsoon climate averaging 573.89 millimeters of annual precipitation. The team tracked four treatments from 2021 to 2025: no nitrogen input, conventional chemical nitrogen at 180 kilograms per hectare, and two regimes in which 25 percent of that nitrogen was replaced with either pig manure or commercial organic fertilizer. All plots received equal phosphorus and potassium, and the crop, cultivar Jinmai 47, was grown without irrigation under no-till management, exactly as local smallholders do.</p>
<p>What makes the study unusual is its insistence that fertilizer source matters, not merely fertilizer quantity. Pig manure and commercial organic product differ in raw material composition, maturity, carbon-to-nitrogen ratio, decomposition rate, and the timing of nutrient release. Those differences, the researchers hypothesized, would ripple through the soil profile, altering how water and nitrate are stored and distributed, how wheat roots explore the soil, and ultimately how yield responds when the sky withholds or delivers rain. To test this, the team classified each season by a drought index: 2021–2022 and 2023–2024 were wet, 2022–2023 normal, and 2024–2025 dry.</p>
<p>The yield data tell a striking story. Nitrogen application lifted grain yields by 44 to 83 percent over unfertilized controls, but the organic substitutions consistently beat chemical fertilizer alone. In the dry year, manure substitution raised yield by 10.32 percent, net income by 32.19 percent, and the benefit–cost ratio by 10.68 percent relative to chemical nitrogen. Manure also produced the highest yields and returns in normal and wet years, reaching 6,395 kilograms per hectare and 9,021 CNY per hectare in wet seasons. In drought, when chemical-only plots fell to 3,674 kilograms per hectare, manure plots held at 4,097 — a buffer against climatic shock that commercial organic fertilizer only partially matched.</p>
<p>Beneath the surface, the mechanisms were physical and measurable. Manure substitution increased mean weight diameter of soil aggregates and water-stable macroaggregate content while lowering bulk density and fractal dimension, indicators of a looser, better-connected pore network. In the top 20 centimeters, manure boosted soil organic matter by 20.27 percent and total nitrogen by 17.57 percent over chemical fertilization, and across the 0–60 centimeter profile the gains reached 21.55 and 19.22 percent. Better aggregates mean better infiltration and water-holding capacity — a critical asset when precipitation arrives in stingy, erratic pulses.</p>
<p>The vertical distribution of water and nitrate revealed perhaps the most intriguing source-specific signature. Both organic treatments enhanced deep soil water storage at 130–200 centimeters, but manure plots accumulated less nitrate-nitrogen than commercial-fertilizer plots across the 0–200 centimeter profile, with a 6.62 percent reduction in the deep 100–200 centimeter layer. The researchers link this to higher root length density under manure in the measured 0–100 centimeter zone: more roots occupying the upper profile potentially intercept more nitrate before it leaches downward. In a region where deep nitrate accumulation signals both wasted fertilizer and groundwater risk, that asymmetry matters.</p>
<p>Root architecture itself responded to the fertilizer regime. Nitrogen application of any kind increased root length density by 28.17 percent and root weight density by 43.16 percent over unfertilized plots, with organic treatments showing generally higher values than chemical alone. Specific root length, a measure of root fineness, fell by more than half in the dry year compared with wet and normal years, reflecting the crop&#8217;s struggle to build absorptive tissue when water is scarce. Precipitation year type shaped everything: root length and weight densities rose 22–64 percent and 33–82 percent respectively in wetter seasons.</p>
<p>To move beyond single indicators, the team deployed two integrative tools. A soil quality index, built from principal component analysis of bulk density, porosity, aggregate stability, organic matter, total nitrogen, and pH, ranked the treatments manure &gt; commercial organic &gt; chemical &gt; no nitrogen, with manure raising the index 73.46 percent over the unfertilized control. A coupling coordination degree model then quantified how well the soil-quality system moved in lockstep with the production-benefit system of yield, net income, and benefit–cost ratio. Coordination exceeded 0.5 — high coordination — under all fertilized treatments except in drought, and manure substitution achieved the highest coordination values, including 0.86 in wet years and a relative advantage over chemical fertilization even in the dry year.</p>
<p>Structural equation modeling tied the threads together. Precipitation acted directly on soil properties but also indirectly by promoting root development, while nitrogen fertilization enhanced production mainly by improving soil physicochemical conditions and root traits. Under manure, yield correlated positively with the soil quality index, coordination degree, net income, and benefit–cost ratio, suggesting the treatment synchronized structural and functional soil improvement with economic output. Notably, soil quality improvements did not always translate into higher water-use efficiency — that conversion depended on the synchrony between nutrient release, root uptake, and precipitation timing, a nuance the authors flag honestly, noting that carbon quality and decomposition dynamics were not directly measured.</p>
<p>The practical message for dryland agriculture is pointed. Where manure is locally available and transport costs are manageable, substituting 25 percent of mineral nitrogen with manure emerges as the most suitable strategy for rainfed winter wheat on the Loess Plateau, offering superior soil rebuilding, deeper water retention, reduced deep nitrate storage, and the strongest drought insurance. The authors caution that long-term environmental effects and the microbial mechanisms behind these responses remain to be fully evaluated. But in an era of intensifying precipitation volatility, the finding that the source of organic nitrogen — not just its amount — governs whether soil improvement becomes farmer income is a lesson that will travel well beyond the yellow earth of Shaanxi.</p>
<p><strong>Subject of Research:</strong> Effects of organic fertilizer source on soil quality and winter wheat production in dryland farming</p>
<p><strong>Article Title:</strong> Organic fertilizer source regulates soil quality–production coordination in dryland winter wheat on the Loess Plateau</p>
<p><strong>Article References:</strong> Lin, Y., Han, Y., Li, Z., Zhang, X., Luo, X., Zhang, Y., Qiang, B., Wang, J., Zhao, X., Liu, E., Ren, X., &amp; Chen, X. (2026). Organic fertilizer source regulates soil quality–production coordination in dryland winter wheat on the Loess Plateau. <em>Journal of Agriculture and Food Research</em>, Article 103366. <a href="https://doi.org/10.1016/j.jafr.2026.103366" rel="noopener noreferrer">https://doi.org/10.1016/j.jafr.2026.103366</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.1016/j.jafr.2026.103366" rel="noopener noreferrer">10.1016/j.jafr.2026.103366</a></p>
<p><strong>Keywords:</strong> dryland agriculture, winter wheat, organic fertilizer, manure substitution, soil quality index, Loess Plateau, nitrogen management, water use efficiency, soil aggregates, drought resilience, coupling coordination, rainfed farming</p>
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		<post-id xmlns="com-wordpress:feed-additions:1">267839</post-id>	</item>
		<item>
		<title>Biochar Supercharges Soil Structure by Rewriting the Invisible Forces Between Particles</title>
		<link>https://scienmag.com/biochar-supercharges-soil-structure-by-rewriting-the-invisible-forces-between-particles/</link>
		
		<dc:creator><![CDATA[Alan Morgan]]></dc:creator>
		<pubDate>Tue, 13 Oct 2026 07:11:45 +0000</pubDate>
				<category><![CDATA[Agriculture]]></category>
		<category><![CDATA[Earth Science]]></category>
		<category><![CDATA[aggregate stability]]></category>
		<category><![CDATA[Biochar]]></category>
		<category><![CDATA[biochar soil amendment]]></category>
		<category><![CDATA[biochar's role in erosion resistance]]></category>
		<category><![CDATA[carbon sequestration]]></category>
		<category><![CDATA[carbon sequestration through biochar]]></category>
		<category><![CDATA[effects of crop residue-derived biochar]]></category>
		<category><![CDATA[electrostatic repulsion]]></category>
		<category><![CDATA[field simulation of biochar application]]></category>
		<category><![CDATA[impact of biochar on soil aggregates]]></category>
		<category><![CDATA[nanometer-scale soil physical forces]]></category>
		<category><![CDATA[organic carbon in soil stabilization]]></category>
		<category><![CDATA[organic carbon regulators in soil stability]]></category>
		<category><![CDATA[particulate organic carbon]]></category>
		<category><![CDATA[readily oxidized organic carbon]]></category>
		<category><![CDATA[soil aggregates]]></category>
		<category><![CDATA[soil electrochemistry]]></category>
		<category><![CDATA[soil erosion]]></category>
		<category><![CDATA[soil health indicators and biochar]]></category>
		<category><![CDATA[soil internal forces]]></category>
		<category><![CDATA[soil organic carbon]]></category>
		<category><![CDATA[soil structure enhancement]]></category>
		<category><![CDATA[van der Waals attraction]]></category>
		<category><![CDATA[water retention in drought-prone soils]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=267071</guid>

					<description><![CDATA[A year-long field experiment in China shows that biochar stabilizes soil aggregates by raising readily oxidized and particulate organic carbon, which reshape surface electrochemistry to boost van der Waals attraction and curb electrostatic repulsion between particles.]]></description>
										<content:encoded><![CDATA[<p>Beneath every farm field lies an architecture most people never think about: a labyrinth of soil crumbs, or aggregates, whose strength determines whether land resists erosion, holds water during drought, and locks away carbon for decades. A new study published in the journal SOIL has now pulled back the curtain on exactly how biochar, the charcoal-like amendment made from crop residues, strengthens that architecture. The answer, it turns out, lies in a hidden tug-of-war of physical forces operating at distances measured in nanometers, and in two specific forms of organic carbon that act as master regulators of the entire system.</p>
<p>The research team, led by Xiaoshuai Song and corresponding author Feinan Hu of Northwest A&amp;F University and the Chinese Academy of Sciences, conducted a field simulation experiment in Yangling, Shaanxi Province, on calcareous Cambisol soil known locally as Lou soil. They applied two kinds of biochar, one made from maize straw and one from wheat straw, at rates ranging from 1 percent to 10 percent by mass, mixed into the top 20 centimeters of soil across 27 experimental plots. They then tracked the soil for 180 and 365 days, measuring not only conventional indicators of soil health but also the electrochemical properties of particle surfaces and the mechanical forces that soil particles exert on one another.</p>
<p>The forces in question are what soil scientists call soil internal forces. When two soil particles sit close together in water, they experience van der Waals attraction, a universal quantum-mechanical pull; electrostatic repulsion, generated by like negative charges on particle surfaces; and surface hydration repulsion, a short-range push created by tightly bound water films. Theoretically, these forces can reach hundreds of thousands of atmospheres between adjacent particles. Whether soil crumbs hold together or disintegrate in rain depends on the balance among them: strong net attraction means stability, while strong net repulsion means aggregates shatter into fine particles that wash away.</p>
<p>The team found that biochar shifted this balance decisively toward cohesion. As application rates increased, biochar raised the soil&#8217;s specific surface area and its surface charge number, with the highest doses boosting specific surface area by more than 90 percent and surface charge number by up to 46 percent. Counterintuitively, adding more charged surface actually reduced electrostatic repulsion between particles, because the surface charge density, the charge spread over each unit of area, declined as organic material coated mineral surfaces. At the same time, biochar increased the Hamaker constant, the material property that governs van der Waals attraction, so particles pulled on each other more strongly. The net interparticle pressure, the sum of all repulsive and attractive components, therefore fell as biochar doses climbed.</p>
<p>But what made the study truly revealing was the identification of which carbon fractions were doing the regulatory work. Soils contain a spectrum of active organic carbon pools: light fraction organic carbon, dissolved organic carbon, particulate organic carbon, and readily oxidized organic carbon. All four surged after biochar addition, in some cases dramatically. At the 10 percent application rate, light fraction organic carbon rose roughly 148 times above the control under maize straw biochar and 127 times under wheat straw biochar, while particulate organic carbon climbed more than 80-fold. Yet statistical analysis showed that readily oxidized organic carbon and particulate organic carbon were the primary drivers, together explaining around two-thirds of the variation in the soil&#8217;s surface electrochemical properties.</p>
<p>The chemistry behind this preference is elegant. Readily oxidized organic carbon is rich in oxygen-containing functional groups such as carboxyl and hydroxyl groups, which carry negative charges and are preferentially adsorbed onto mineral surfaces, expanding the electrical double layer and reshaping the electrostatic landscape around each particle. Particulate organic carbon, by contrast, is coarser plant-derived debris that works more slowly, binding physically to fine particles and forming stable mineral-organic complexes. The researchers suggest the two fractions operate on complementary timescales: readily oxidized carbon responds quickly to management changes, while particulate carbon exerts its influence over longer periods through durable organo-mineral associations.</p>
<p>Time proved to be another crucial variable. Over the first 180 days, the absolute contents of active carbon fractions actually declined as microbes consumed labile material and stabilized the remainder, yet the electrochemical parameters kept climbing, and the benefits to aggregate stability grew stronger. By 365 days, the improvement in aggregate stability exceeded that seen at 180 days. The explanation lies in the relative magnitudes of the forces: as biochar aged and its carbon integrated with minerals, both the Hamaker constant and the surface properties increased, but the gain in van der Waals attraction far outpaced the modest rise in electrostatic repulsion, producing a progressively lower net repulsive force and therefore tougher aggregates.</p>
<p>To connect these nanoscale forces to field-scale outcomes, the team measured soil aggregate breaking strength, defined by the mass of fine particles below 5 and 10 micrometers released when macroaggregates disintegrate in sodium chloride solutions of varying concentration. As electrolyte concentration dropped, breaking strength rose sharply before leveling off, with 10 to the power of minus 2 moles per liter marking a clear tipping point for aggregate disintegration. Crucially, at every concentration, higher biochar rates meant lower breaking strength, meaning less crumbling. Regression analysis confirmed that aggregate breaking strength rose exponentially with net interparticle pressure, cementing the causal chain from carbon fractions to surface electrochemistry to internal forces to structural stability.</p>
<p>The practical implications are considerable. Soil degradation and erosion threaten agricultural sustainability worldwide, and biochar has long been promoted for its carbon sequestration potential. This study adds a mechanistic foundation for a more targeted use: rather than treating biochar as a generic soil improver, farmers and soil managers could select or engineer biochars specifically to boost readily oxidized and particulate organic carbon, thereby tuning the internal forces that glue soil together. Notably, maize and wheat straw biochars performed nearly identically at equal doses, suggesting that feedstock choice matters less than application rate in this calcareous system, with benefits amplifying over time rather than fading.</p>
<p>The authors are careful to note limitations. Their measurements used sodium-saturated samples, a simplification compared with natural soils containing multiple exchangeable cations, so the quantified forces represent a mechanistic assessment rather than a direct portrait of field conditions. The experiment also spans only one year, while biochar is known to persist in soil for years to decades. Still, the findings open a striking window onto processes invisible to the naked eye: every clod of earth in a biochar-amended field is held together by quantum attraction strengthened and electrostatic repulsion tamed, all orchestrated by two humble fractions of organic carbon that turn out to be the quiet architects of fertile ground.</p>
<p><strong>Subject of Research:</strong> Biochar effects on soil aggregate stability through active organic carbon fractions and soil internal forces</p>
<p><strong>Article Title:</strong> Biochar addition enhances soil aggregate stability by modulating soil internal forces: the critical role of readily oxidized organic carbon and particulate organic carbon</p>
<p><strong>Article References:</strong> Song, X., Xu, C., Zhao, H., Li, J., Du, W., Ding, W., Yu, Z., Zhang, F., &amp; Hu, F. (2026). Biochar addition enhances soil aggregate stability by modulating soil internal forces: the critical role of readily oxidized organic carbon and particulate organic carbon. <em>SOIL, 12</em>(2), 963-978. <a href="https://doi.org/10.5194/soil-12-963-2026" rel="noopener noreferrer">https://doi.org/10.5194/soil-12-963-2026</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.5194/soil-12-963-2026" rel="noopener noreferrer">10.5194/soil-12-963-2026</a></p>
<p><strong>Keywords:</strong> biochar, soil aggregates, soil internal forces, van der Waals attraction, electrostatic repulsion, readily oxidized organic carbon, particulate organic carbon, soil electrochemistry, aggregate stability, soil erosion, carbon sequestration, soil organic carbon</p>
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		<post-id xmlns="com-wordpress:feed-additions:1">267071</post-id>	</item>
		<item>
		<title>Organic Fertilizer Plus Cellulose Additive Rebuilds Sandy Desert Soil and Lifts Cotton Yields in Xinjiang</title>
		<link>https://scienmag.com/organic-fertilizer-plus-cellulose-additive-rebuilds-sandy-desert-soil-and-lifts-cotton-yields-in-xinjiang/</link>
		
		<dc:creator><![CDATA[Alan Morgan]]></dc:creator>
		<pubDate>Fri, 09 Oct 2026 07:13:55 +0000</pubDate>
				<category><![CDATA[Agriculture]]></category>
		<category><![CDATA[biological soil recovery]]></category>
		<category><![CDATA[cellulose additive]]></category>
		<category><![CDATA[cotton yield]]></category>
		<category><![CDATA[cotton yield enhancement]]></category>
		<category><![CDATA[crop productivity in degraded soils]]></category>
		<category><![CDATA[field study on soil amendments]]></category>
		<category><![CDATA[Organic fertilizer]]></category>
		<category><![CDATA[path modeling]]></category>
		<category><![CDATA[root vigor]]></category>
		<category><![CDATA[sandy desert soil improvement]]></category>
		<category><![CDATA[sandy soil]]></category>
		<category><![CDATA[sodium carboxymethyl cellulose]]></category>
		<category><![CDATA[soil aggregates]]></category>
		<category><![CDATA[soil bulk density]]></category>
		<category><![CDATA[soil organic carbon]]></category>
		<category><![CDATA[soil quality]]></category>
		<category><![CDATA[soil restoration techniques]]></category>
		<category><![CDATA[soil stabilization with biodegradable polymers]]></category>
		<category><![CDATA[sustainable agriculture]]></category>
		<category><![CDATA[sustainable agriculture in Xinjiang]]></category>
		<category><![CDATA[water retention in sandy soils]]></category>
		<category><![CDATA[Xinjiang]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=252469</guid>

					<description><![CDATA[A three-year field experiment in southern Xinjiang shows that combining organic fertilizer with sodium carboxymethyl cellulose rebuilds sandy soil structure, boosts root vigor and raises cotton yields by up to nearly 17 percent.]]></description>
										<content:encoded><![CDATA[<p>In the desert oasis farmland of southern Xinjiang, one of China&#8217;s most important cotton-producing regions, the soil itself has long been the enemy of the harvest. Sandy soils with fragile, poorly cemented particles hold neither water nor nutrients well, so every irrigation event risks leaching fertilizer beyond the reach of roots, and every dry spell drains the profile of moisture that crops depend on. A new three-year field study published in the journal Plant and Soil reports that a simple pairing of two amendments, organic fertilizer and sodium carboxymethyl cellulose, can rebuild the physical and biological fabric of these degraded soils and translate that repair directly into higher cotton yields.</p>
<p>The research, led by Xiaoxian Duan, Quanjiu Wang, Weiyi Mu and colleagues at Xi&#8217;an University of Technology, set out to test whether the two amendments work better together than either alone. Organic fertilizer supplies carbon, nutrients and microbial substrate, while sodium carboxymethyl cellulose, or CMC-Na, is a water-soluble, biodegradable polymer derived from cellulose that can bind soil particles, improve water retention and stabilize aggregates. The team reasoned that the polymer could provide the structural scaffolding that sandy soils lack, while the organic fertilizer would fuel the biological and chemical recovery, and that the combination might unlock synergies neither material could achieve on its own.</p>
<p>To test this, the researchers ran a continuous three-year field experiment in southern Xinjiang, comparing plots treated with organic fertilizer alone, CMC-Na alone, and the two applied together, against untreated control plots. They systematically evaluated soil physical properties, enzyme activities, organic carbon content and the availability of nitrogen, phosphorus and potassium throughout the top 40 centimeters of the soil profile. The most striking improvements appeared in the 0 to 20 centimeter topsoil layer, the zone where cotton roots are most active and where drip irrigation and fertilization concentrate their effects.</p>
<p>The numbers from the optimal combined treatment, labeled O2C2, are substantial. Compared with the control, soil bulk density, a measure of how tightly packed and compacted the soil is, decreased by 7.00 to 8.54 percent. Lower bulk density means looser soil, easier root penetration and more space for air and water. At the same time, total porosity rose by 9.33 to 11.93 percent, and the content of water-stable aggregates larger than 0.25 millimeters, the small clumps of soil that resist being washed apart and that underpin healthy soil structure, increased by 13.86 to 15.08 percent. Available water content, the reservoir of moisture plants can actually draw on, climbed by 13.50 to 14.52 percent.</p>
<p>The chemical and biological changes were equally dramatic. Soil organic carbon, the backbone of soil fertility and a key indicator of long-term soil health, surged by 72.76 to 90.35 percent under the combined treatment, while alkali-hydrolyzable nitrogen, a measure of the nitrogen readily available to plants, rose by 23.15 to 28.83 percent. The researchers also tracked soil enzyme activities, which reflect the intensity of microbial processes that cycle nutrients through the soil, and found that the combined treatment maximized the overall soil quality index, a composite score integrating physical, chemical and biological indicators.</p>
<p>Crucially, the soil improvements were not merely cosmetic. Cotton plants growing in the amended soils showed markedly better root vigor, a measure of the physiological activity and health of the root system, which increased by 14.36 to 25.79 percent relative to the control. Vigorous roots are the engine of crop productivity in arid environments, because they determine how effectively a plant can capture water and nutrients from a finite and often hostile soil volume. The enhanced root performance translated into a 13.01 to 16.79 percent increase in seed cotton yield, the raw harvested product before ginning.</p>
<p>To understand which changes mattered most, the team applied partial least squares path modeling, a statistical technique that can trace how different sets of variables influence one another along hypothesized causal chains. The analysis revealed that the improvement of topsoil physical properties was the primary driver of the overall soil quality enhancement, with a path coefficient of 0.776, indicating a very strong influence. In other words, the structural repair of the sandy soil, its loosened density, increased porosity and stabilized aggregates, was the foundation on which the chemical and biological gains were built.</p>
<p>The path modeling also identified the core mechanism linking soil treatment to harvest: a sequential pathway running from soil quality index to root vigor and finally to yield. Better soil structure and fertility create a more favorable habitat for roots; healthier, more active roots capture more water and nutrients; and better-supplied plants produce more cotton. This chain, the authors conclude, is the mechanism by which co-application of organic fertilizer and CMC-Na sustains stable, high cotton yields in sandy agroecosystems, by optimizing physical structures and simultaneously activating the nutrient and biological dynamics of the soil.</p>
<p>The findings carry weight well beyond a single experimental field. Southern Xinjiang&#8217;s cotton belt relies heavily on mulched drip irrigation, a system that delivers water and fertilizer precisely but that depends on the soil being able to retain and redistribute what it receives. In coarse sandy soils, that retention is the weak link, and previous studies by overlapping research groups have explored related strategies, including combining carboxymethyl cellulose with biochar to improve water retention and aggregate stability in desert soils, and applying the polymer in coastal saline-alkali croplands. The new work extends this line of research by quantifying, over three consecutive seasons, how the polymer performs when paired with organic fertilizer and by formally modeling the causal chain from soil physics to crop yield.</p>
<p>For farmers and soil managers in arid regions, the study suggests that amending sandy soils is most effective when structural and biological interventions are combined rather than applied in isolation. The cellulose-based additive addresses the physical fragility that makes sandy soils leak water and nutrients, while the organic fertilizer rebuilds the carbon reserves and microbial activity that sustain nutrient supply over time. Because CMC-Na is biodegradable and organic fertilizers can be produced from agricultural and animal waste, the approach also aligns with broader goals of sustainable agriculture, turning a waste-derived polymer and recycled nutrients into a durable upgrade of one of the world&#8217;s most challenging farming environments. As cotton remains a cornerstone of the regional economy, the demonstration that a 13 to 17 percent yield gain can be achieved by repairing the soil itself offers a practical blueprint for sustaining production on fragile desert farmland.</p>
<p><strong>Subject of Research:</strong> Co-application of organic fertilizer and sodium carboxymethyl cellulose to improve sandy soil quality and cotton yield in southern Xinjiang</p>
<p><strong>Article Title:</strong> Co-application of organic fertilizer and sodium carboxymethyl cellulose improves soil quality and root vigor to sustain cotton yield in sandy fields of southern Xinjiang</p>
<p><strong>Article References:</strong> Duan, X., Wang, Q., Mu, W., Ma, C., Sun, Y., &amp; Su, L. (2026). Co-application of organic fertilizer and sodium carboxymethyl cellulose improves soil quality and root vigor to sustain cotton yield in sandy fields of southern Xinjiang. <em>Plant and Soil</em>. <a href="https://doi.org/10.1007/s11104-026-09141-y" rel="noopener noreferrer">https://doi.org/10.1007/s11104-026-09141-y</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.1007/s11104-026-09141-y" rel="noopener noreferrer">10.1007/s11104-026-09141-y</a></p>
<p><strong>Keywords:</strong> soil quality, organic fertilizer, sodium carboxymethyl cellulose, cotton yield, sandy soil, soil aggregates, root vigor, soil organic carbon, soil bulk density, path modeling, Xinjiang, sustainable agriculture</p>
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		<post-id xmlns="com-wordpress:feed-additions:1">252469</post-id>	</item>
		<item>
		<title>Hidden Fungus Inside Ryegrass Rewrites the Microbial Map of Soil, Aggregate by Aggregate</title>
		<link>https://scienmag.com/hidden-fungus-inside-ryegrass-rewrites-the-microbial-map-of-soil-aggregate-by-aggregate/</link>
		
		<dc:creator><![CDATA[Morgan Morrow]]></dc:creator>
		<pubDate>Thu, 08 Oct 2026 22:58:43 +0000</pubDate>
				<category><![CDATA[Agriculture]]></category>
		<category><![CDATA[amplicon sequencing]]></category>
		<category><![CDATA[co-occurrence networks]]></category>
		<category><![CDATA[effects of soil aggregate size on microbial diversity]]></category>
		<category><![CDATA[Epichloë endophyte]]></category>
		<category><![CDATA[foliar endophyte contribution to underground microbial ecology]]></category>
		<category><![CDATA[fungal ecology]]></category>
		<category><![CDATA[impact]]></category>
		<category><![CDATA[impact of Epichloë festucae on soil aggregate microhabitats]]></category>
		<category><![CDATA[influence of plant-associated fungi on soil physicochemical properties]]></category>
		<category><![CDATA[microbial communities]]></category>
		<category><![CDATA[microbial interactions within soil microhabitats affected by ryegrass fungus]]></category>
		<category><![CDATA[microbiome]]></category>
		<category><![CDATA[nitrogen cycling]]></category>
		<category><![CDATA[perennial ryegrass]]></category>
		<category><![CDATA[plant-soil feedbacks]]></category>
		<category><![CDATA[relationship between plant endophytes and soil aggregate stability]]></category>
		<category><![CDATA[role of plant-fungal symbiosis in soil microbial restructuring]]></category>
		<category><![CDATA[soil aggregates]]></category>
		<category><![CDATA[soil enzymes]]></category>
		<category><![CDATA[Soil microbial community dynamics influenced by endophytic fungus in ryegrass]]></category>
		<category><![CDATA[soil organic carbon]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=250245</guid>

					<description><![CDATA[A new study in Plant and Soil shows that the foliar fungus Epichloë festucae reshapes bacterial and fungal communities across soil aggregate size fractions in ryegrass fields, altering diversity gradients, network complexity and stability.]]></description>
										<content:encoded><![CDATA[<p>Deep inside the leaves of perennial ryegrass lives a microscopic tenant that never touches the soil, yet according to a new study it can reorganize the entire underground world beneath the plant. The fungus, Epichloë festucae, is a foliar endophyte: it grows systemically through the tissues of its grass host, feeding on plant sugars and, in return, producing compounds that deter herbivores and boost stress tolerance. For decades, ecologists have studied this partnership from the plant&#8217;s point of view. But a research team led by Chao Wang, Jie Jin, Yang Yang and Jianfeng Wang, publishing in the journal Plant and Soil, has now traced the fungus&#8217;s influence all the way down into the soil itself, revealing that its effects are not uniform. Instead, they vary dramatically depending on the size of the soil aggregates, the crumbs of mineral and organic matter that form the architecture of the underground world.</p>
<p>Soil is not a homogeneous soup of microbes. It is a labyrinth of aggregates ranging from fine microaggregates smaller than a quarter of a millimeter to chunky macroaggregates larger than two millimeters. Each size class creates a distinct microhabitat, with different pore sizes, oxygen availability, water retention and access to organic matter. Microaggregates offer protected niches where slow-growing specialists thrive, while macroaggregates, held together by fungal hyphae and plant roots, are hotspots of decomposition and nutrient cycling. Previous work has shown that microbial diversity often differs across these fractions, but almost nothing was known about how a symbiotic fungus living entirely inside plant shoots could alter those patterns. The new study set out to answer exactly that question.</p>
<p>The experiment took advantage of a long-term field setup in which perennial ryegrass, Lolium perenne, had been grown for five years in plots containing plants either infected with Epichloë festucae, designated E+, or endophyte-free, designated E−. After five growing seasons, the researchers sampled the soils beneath both plot types and physically separated the aggregates into four size fractions: less than 0.25 millimeters, 0.25 to 1 millimeter, 1 to 2 millimeters, and greater than 2 millimeters. From each fraction they extracted DNA and used amplicon sequencing to catalog the bacterial and fungal communities, then related those communities to a suite of soil physicochemical measurements, including nitrogen fractions, soil organic carbon and enzyme activities such as catalase.</p>
<p>The first striking result concerned biodiversity gradients. In soils from endophyte-free ryegrass, both bacterial and fungal diversity, measured with the Shannon index, and species richness, measured with the Chao1 index, declined steadily as aggregate size increased. This pattern suggests that in uninfected soils, the smallest aggregates act as reservoirs of microbial diversity, while the larger, more aerated crumbs support fewer species. But in soils beneath endophyte-infected plants, this decline was noticeably attenuated. The presence of the fungus inside the grass somehow smoothed out the diversity differences between aggregate classes, implying that the plant&#8217;s internal symbiont homogenizes the microbial landscape across physical niches that would otherwise diverge.</p>
<p>Community composition told a similar story. Using Adonis analysis, a multivariate statistical test that measures how strongly communities differ among groups, the researchers found that bacterial community dissimilarity among aggregate fractions was reduced under endophyte infection. In other words, without the endophyte, each aggregate size class harbored a distinct bacterial assemblage; with the endophyte, those assemblages became more alike. This convergence is significant because it suggests the infected plants are altering the inputs that drive microbial differentiation among aggregates, most likely through changes in root exudates, litter chemistry and rhizodeposition, the fluxes of carbon and nitrogen that plants pump into the soil and that differ between aggregate microhabitats.</p>
<p>The team then turned to co-occurrence network analysis, which maps the potential ecological interactions among microbial taxa and reveals how complex and interconnected each community is. In endophyte-free soils, network complexity generally increased with aggregate size, meaning the largest crumbs hosted the most densely connected microbial webs. Under endophyte infection, however, the picture changed in a taxon-specific way. Bacterial networks peaked in complexity in the 1 to 2 millimeter fraction, while fungal networks showed the opposite pattern, with their most intricate connections occurring in smaller aggregates. These shifts indicate that the endophyte does not simply add or remove species; it rewires who interacts with whom, and it does so differently for bacteria and fungi.</p>
<p>Perhaps the most consequential findings came from measures of community cohesion and stability. In endophyte-free soils, bacterial cohesion, a metric quantifying the degree of connectedness among taxa, was positively correlated with aggregate size, while community stability was negatively correlated with it. Large aggregates in uninfected soils therefore hosted tightly linked but fragile bacterial communities. In endophyte-infected soils, both relationships were disrupted, breaking the predictable coupling between physical structure and microbial network properties. Because network stability is thought to underpin the resilience of soil functions such as decomposition and nutrient cycling, this decoupling suggests that endophyte infection could fundamentally alter how soil ecosystems respond to disturbance, though the long-term functional consequences remain to be tested.</p>
<p>The chemical fingerprints of the endophyte&#8217;s influence were equally clear. Mantel tests, which correlate community composition with environmental variables, showed that bacterial communities in endophyte-infected soils were associated with ammonium nitrogen, nitrate nitrogen and catalase activity, whereas in endophyte-free soils they were associated mainly with total nitrogen and catalase. This shift implicates the nitrogen cycle as a key pathway of endophyte influence, consistent with earlier work by some of the same authors showing that Epichloë infection alters nitrifier and denitrifier communities during host litter decomposition. Structural equation modeling using partial least squares went further, indicating that the associations between the endophyte and fungal diversity were linked to variations in soil nitrate nitrogen and soil organic carbon, pointing to carbon and nitrogen transformations as the mechanistic bridge between a leaf-dwelling fungus and the soil microbiome.</p>
<p>Why should a fungus that never leaves the plant have such reach into the soil? The most plausible explanation lies in the plant-mediated pathway. Epichloë infection changes host physiology: it alters alkaloid production, growth rates, root architecture and the quantity and quality of carbon released through roots and returned through decomposing litter. Over five years of cultivation, these altered inputs accumulate differently in different aggregate fractions, since macroaggregates receive fresh litter and root residues while microaggregates hold older, chemically stabilized organic matter. The endophyte effectively reprograms the resource landscape, and the microbial communities in each aggregate class respond accordingly. Prior studies had already shown that endophyte-infected grasses change rhizosphere communities and soil enzyme activities; the new work extends that influence into the physically structured interior of the soil.</p>
<p>The implications reach well beyond ryegrass pastures. Soil aggregates are increasingly recognized as the biologically relevant scale at which microbial processes occur, and models of carbon sequestration and greenhouse gas emissions depend on assumptions about where in the soil matrix particular microbes live and work. If a heritable, vertically transmitted fungal symbiont can reshape microbial diversity, network architecture and stability across aggregate fractions, then breeding or inoculating forage grasses with specific endophyte strains becomes a potential lever for managing soil function. The authors emphasize that their study provides a basis for predicting soil functional shifts under endophyte infection, and the raw sequence data have been deposited in a public archive for further analysis. What began as a story about a fungus protecting a grass from herbivores has become a story about how one intimate symbiosis can ripple outward, crumb by crumb, through the hidden architecture of the soil.</p>
<p><strong>Subject of Research:</strong> Effects of foliar Epichloë endophyte infection on soil microbial communities across aggregate size fractions in ryegrass soils</p>
<p><strong>Article Title:</strong> Foliar Epichloë endophyte infection reshapes soil microbial communities across aggregate size fractions in ryegrass soils</p>
<p><strong>Article References:</strong> Wang, C., Jin, J., Liu, R., Zhang, D., Ma, B., Zhang, S., Yang, Y., &amp; Wang, J. (2026). Foliar Epichloë endophyte infection reshapes soil microbial communities across aggregate size fractions in ryegrass soils. <em>Plant and Soil</em>. <a href="https://doi.org/10.1007/s11104-026-09092-4" rel="noopener noreferrer">https://doi.org/10.1007/s11104-026-09092-4</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.1007/s11104-026-09092-4" rel="noopener noreferrer">10.1007/s11104-026-09092-4</a></p>
<p><strong>Keywords:</strong> Epichloë endophyte, perennial ryegrass, soil aggregates, microbial communities, amplicon sequencing, co-occurrence networks, soil organic carbon, nitrogen cycling, soil enzymes, fungal ecology, plant-soil feedbacks, microbiome</p>
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		<post-id xmlns="com-wordpress:feed-additions:1">250245</post-id>	</item>
		<item>
		<title>Less Nitrogen, More Carbon: Straw Trick Turns Saline Soils into Carbon Sinks</title>
		<link>https://scienmag.com/less-nitrogen-more-carbon-straw-trick-turns-saline-soils-into-carbon-sinks/</link>
		
		<dc:creator><![CDATA[Alan Morgan]]></dc:creator>
		<pubDate>Wed, 07 Oct 2026 11:57:10 +0000</pubDate>
				<category><![CDATA[Agriculture]]></category>
		<category><![CDATA[bacterial community]]></category>
		<category><![CDATA[carbon sequestration]]></category>
		<category><![CDATA[climate change mitigation through soil carbon]]></category>
		<category><![CDATA[coastal saline agriculture]]></category>
		<category><![CDATA[crop rotation and soil health]]></category>
		<category><![CDATA[crop straw incorporation]]></category>
		<category><![CDATA[enzyme stoichiometry]]></category>
		<category><![CDATA[impacts of reduced fertilizer use]]></category>
		<category><![CDATA[innovative saline soil farming techniques]]></category>
		<category><![CDATA[microbial nitrogen mining]]></category>
		<category><![CDATA[nitrogen fertilization]]></category>
		<category><![CDATA[nitrogen fertilizer reduction]]></category>
		<category><![CDATA[organic carbon storage in saline soils]]></category>
		<category><![CDATA[saline soil]]></category>
		<category><![CDATA[Saline soil carbon sequestration]]></category>
		<category><![CDATA[saline soil management]]></category>
		<category><![CDATA[saline soil remediation]]></category>
		<category><![CDATA[soil aggregates]]></category>
		<category><![CDATA[soil microbiology]]></category>
		<category><![CDATA[soil organic carbon]]></category>
		<category><![CDATA[straw incorporation]]></category>
		<category><![CDATA[sustainable agriculture]]></category>
		<category><![CDATA[sustainable farming practices]]></category>
		<category><![CDATA[Yellow River Delta]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=244345</guid>

					<description><![CDATA[A three-year field experiment in China's Yellow River Delta shows that pairing reduced nitrogen fertilizer with half-dose straw incorporation boosts soil organic carbon sequestration in saline soils by shifting microbial metabolism toward carbon stabilization.]]></description>
										<content:encoded><![CDATA[<p>Salt-affected soils blanket more than one billion hectares of the Earth&#8217;s surface, a vast and often written-off expanse of farmland that farmers struggle to make productive and scientists have long struggled to understand. Now a three-year field experiment in China&#8217;s Yellow River Delta suggests that these marginal soils may hide an unexpected climate opportunity, and that unlocking it requires doing something counterintuitive: applying less fertilizer, not more. The study, published in the journal Plant and Soil, found that combining a modestly reduced dose of nitrogen fertilizer with a half-rate of incorporated crop straw pushed a coastal saline soil to sequester organic carbon more efficiently than the conventional high-input regime that farmers typically rely on.</p>
<p>The research team, led by Zhichang Jing of Qingdao Agricultural University together with colleagues from Shandong Huibang Bohai Agriculture Development Limited Company, ran their experiment under a winter wheat–summer maize rotation, the dominant double-cropping system of the region. They compared two nitrogen levels, a conventional 270 kilograms of nitrogen per hectare and a reduced rate of 210 kilograms per hectare, crossed with three straw incorporation rates: no straw at all, 5,000 kilograms per hectare, and 10,000 kilograms per hectare. Over three years they tracked how each combination reshaped the soil&#8217;s physical architecture, its chemistry, its enzyme machinery, and ultimately the bacterial communities that govern whether carbon entering the soil is locked away or breathed back out into the atmosphere as carbon dioxide.</p>
<p>The standout treatment was the one the researchers labeled N2S1, the reduced nitrogen dose paired with the half-rate straw application. This combination achieved the highest soil organic carbon sequestration efficiency of any treatment tested, outperforming the conventional high-input practice of full nitrogen with full straw by 6.4 percent. That margin may sound modest, but in the world of soil carbon accounting, where gains of even a few percent over whole rotations are considered meaningful, a 6.4 percent improvement achieved while cutting fertilizer use is a striking result. It means more of the carbon in the straw ended up stored in the soil rather than lost, and it was accomplished with 60 kilograms less nitrogen per hectare each year.</p>
<p>What makes the finding technically interesting is the mechanism the authors uncovered. The winning treatment did not simply dump more carbon into the ground. Instead, it changed the fate of the carbon that was already flowing through the system. Soils under the reduced-nitrogen, half-straw regime developed more large macro-aggregates, the soil clumps larger than two millimeters that act as tiny vaults, physically shielding organic matter from decomposer microbes. The team also detected a shift toward more recalcitrant carbon fractions, the chemically stubborn forms of organic matter that resist breakdown for years or decades. Infrared analysis of organic carbon functional groups confirmed this chemical hardening of the soil&#8217;s carbon stock.</p>
<p>The key to this transformation, the researchers argue, lies in microbial stoichiometry, the balancing act microbes perform between the carbon and nitrogen available in their food. When nitrogen became scarcer under the reduced application rate, soil enzymes told a clear story: the ratio of carbon-acquiring to nitrogen-acquiring extracellular enzyme activity rose from 0.393 under the conventional treatment to 0.414 under the reduced-nitrogen regime, signaling intensified microbial nitrogen limitation. Faced with a nitrogen shortage, the microbial community ramped up its carbon-cycling enzymes, with xylanase activity increasing by 15.9 percent and beta-glucosidase by 13.2 percent. This pattern fits what soil ecologists call microbial nitrogen mining, a strategy in which microbes invest extra enzymatic effort to extract nitrogen from organic matter, and in doing so process carbon more thoroughly and incorporate it more efficiently into their own biomass and residues.</p>
<p>DNA sequencing of the soil bacterial communities added a second layer of evidence. Under the optimal treatment, the community shifted toward oligotrophic taxa, the patient, slow-growing specialists such as Acidobacteriota and Chloroflexi that thrive when nutrients are scarce rather than abundant. These are precisely the organisms that tend to convert carbon into stable microbial necromass rather than releasing it quickly through respiration. Network analysis of the community revealed something equally telling: the bacteria under the reduced-input treatment formed a more complex and cooperative co-occurrence network, with more connections linking species to one another. A richer web of microbial interactions is often associated with more stable ecosystem functioning and more efficient resource cycling, suggesting the treatment did not just change who lived in the soil but how the residents worked together.</p>
<p>The broader significance of the study lies in the sheer scale of the resource at stake. Saline and salt-affected soils are among the most extensive degraded land types on the planet, and much of that area sits in agricultural regions where straw burning or removal is common practice. Incorporating straw into such soils has long been promoted as a way to build organic matter, but it carries a well-known risk: fresh crop residues can stimulate microbes to decompose existing soil organic carbon as well, a phenomenon called priming that can erase the intended gains. High nitrogen availability is thought to worsen this problem by relieving the microbial nitrogen limitation that would otherwise force careful, conservative carbon processing. The new results suggest that deliberately maintaining a degree of nitrogen scarcity, calibrated against the carbon-to-nitrogen ratio of the added straw, can tip the balance away from respiratory carbon loss and toward stabilization.</p>
<p>There are also practical and economic dimensions worth noting. Nitrogen fertilizer is one of the largest recurring costs in cereal production and a major source of agriculture&#8217;s greenhouse gas footprint, both from the energy used to manufacture it and from nitrous oxide emitted from fertilized fields. A management recipe that achieves better carbon sequestration while trimming nitrogen inputs by roughly 22 percent offers a rare double dividend: lower costs for farmers working marginal land and reduced emissions intensity for the cropping system as a whole. Because the approach relies on adjusting rates of two inputs that farmers already manage, rather than requiring new technologies or amendments, it could in principle be adopted widely across salt-affected wheat-maize regions without significant infrastructure investment.</p>
<p>The authors are careful to frame the strategy as biologically driven, and that framing matters. Rather than relying on chemical stabilization or mineral associations alone, the treatment works by steering the soil&#8217;s living community toward a metabolic regime that favors carbon retention. Aggregate formation provides the physical protection, recalcitrant carbon fractions provide the chemical durability, and a nitrogen-limited, cooperative microbial community provides the biological engine that channels straw carbon into both. As the researchers conclude, moderately reduced nitrogen input combined with half-dose straw incorporation optimized the carbon-to-nitrogen stoichiometric balance, redirecting microbial metabolism from respiratory carbon loss toward aggregate-mediated physical protection. For the billion-plus hectares of salt-affected soil worldwide, that is a recipe worth testing far beyond the Yellow River Delta.</p>
<p><strong>Subject of Research:</strong> Soil organic carbon sequestration through straw incorporation and reduced nitrogen fertilization in saline soils</p>
<p><strong>Article Title:</strong> Synergistic straw incorporation and reduced nitrogen application enhance soil carbon sequestration in saline soils</p>
<p><strong>Article References:</strong> Jing, Z., Zhang, L., Han, J., Ma, C., Zhang, S., Sun, H., &amp; Ding, X. (2026). Synergistic straw incorporation and reduced nitrogen application enhance soil carbon sequestration in saline soils. <em>Plant and Soil</em>. <a href="https://doi.org/10.1007/s11104-026-09056-8" rel="noopener noreferrer">https://doi.org/10.1007/s11104-026-09056-8</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.1007/s11104-026-09056-8" rel="noopener noreferrer">10.1007/s11104-026-09056-8</a></p>
<p><strong>Keywords:</strong> soil organic carbon, saline soil, straw incorporation, nitrogen fertilization, microbial nitrogen mining, enzyme stoichiometry, soil aggregates, bacterial community, Yellow River Delta, carbon sequestration, soil microbiology, sustainable agriculture</p>
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		<post-id xmlns="com-wordpress:feed-additions:1">244345</post-id>	</item>
		<item>
		<title>Engineered Carbon Materials Could Lock Climate-Warming Carbon in Farm Soils, Review Finds</title>
		<link>https://scienmag.com/engineered-carbon-materials-could-lock-climate-warming-carbon-in-farm-soils-review-finds/</link>
		
		<dc:creator><![CDATA[Alan Morgan]]></dc:creator>
		<pubDate>Sat, 03 Oct 2026 20:34:32 +0000</pubDate>
				<category><![CDATA[Agriculture]]></category>
		<category><![CDATA[agroecosystems]]></category>
		<category><![CDATA[artificial carbon materials in agriculture]]></category>
		<category><![CDATA[artificial humic substances]]></category>
		<category><![CDATA[bibliometric analysis of soil carbon research]]></category>
		<category><![CDATA[Biochar]]></category>
		<category><![CDATA[carbon sequestration]]></category>
		<category><![CDATA[Climate Change Mitigation]]></category>
		<category><![CDATA[climate change mitigation through soil management]]></category>
		<category><![CDATA[effects of the Paris Agreement on soil carbon studies]]></category>
		<category><![CDATA[Engineered carbon materials for soil carbon sequestration]]></category>
		<category><![CDATA[greenhouse gas emissions]]></category>
		<category><![CDATA[greenhouse gas emissions from farm soils]]></category>
		<category><![CDATA[hydrochar]]></category>
		<category><![CDATA[impact of intensive farming on soil carbon loss]]></category>
		<category><![CDATA[microbial necromass]]></category>
		<category><![CDATA[microbial role in soil carbon storage]]></category>
		<category><![CDATA[mineral association]]></category>
		<category><![CDATA[potential of engineered materials to combat climate warming]]></category>
		<category><![CDATA[priming effect]]></category>
		<category><![CDATA[process-oriented soil carbon research gaps]]></category>
		<category><![CDATA[soil aggregates]]></category>
		<category><![CDATA[soil organic carbon]]></category>
		<category><![CDATA[soil organic carbon enhancement techniques]]></category>
		<category><![CDATA[soil structure degradation due to agriculture]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=231734</guid>

					<description><![CDATA[A major review of 25 years of research finds that biochar, hydrochar and artificial humic substances can boost soil carbon in farmland, but only careful source-tracking reveals whether the gains truly last.]]></description>
										<content:encoded><![CDATA[<p>Soils hold nearly 80 percent of the carbon stored in terrestrial ecosystems, making the dirt beneath our feet one of the planet&#8217;s most important climate allies. Yet decades of intensive agriculture have stripped carbon from many farmed soils, degrading their structure and weakening their capacity to keep carbon out of the atmosphere. A sweeping new review published in the Journal of Agriculture and Food Research examines whether a family of engineered materials, collectively called artificial carbon materials, can help rebuild those carbon stocks, and its conclusions are more nuanced, and more useful, than a simple yes or no.</p>
<p>The review, led by Pengfei Xu and colleagues, analyzed more than 61,000 publications indexed in the Web of Science Core Collection between 2000 and 2025, of which 7,893 focused specifically on soil carbon sequestration. The bibliometric analysis reveals a research field that has grown explosively, with publication output accelerating sharply after the 2016 Paris Agreement. But it also exposes a striking imbalance: outcome-related keywords such as soil organic carbon and greenhouse gas emissions dominate the literature, while process-oriented terms like microbial community, priming effect and adsorption remain far less visible. The authors argue that this gap between what scientists measure and what they explain has left the field without a unified mechanistic framework.</p>
<p>Artificial carbon materials come in three main flavors, each forged from biomass through different thermochemical routes. Biochar, the best studied of the three, is produced by heating biomass above 300 degrees Celsius under oxygen-limited conditions, yielding a carbon-rich, aromatic material. Hydrochar is made through hydrothermal carbonization, which uses water and moderate temperatures and produces a more oxygenated, more microbially accessible substance. Artificial humic substances, the youngest class, are created through alkaline hydrothermal humification, a process that accelerates the chemistry of natural humification and yields oxygen-rich materials resembling natural soil humic acids. The review is careful to keep these classes distinct, noting that they differ profoundly in molecular composition, surface chemistry and likely behavior in soil.</p>
<p>The evidence that these materials raise measured soil organic carbon is generally positive but strikingly heterogeneous. In one 180-day incubation of maize cropland topsoil in Jilin, China, cotton straw-derived biochar applied at equivalent carbon inputs increased soil organic carbon concentration by 94.6 percent, compared with 64.4 percent for raw straw. In a paddy soil column experiment, hydrochar applications increased native soil organic carbon by 1.0 to 3.0 percent while shifting carbon from labile to stable pools. In black soil from Harbin, artificial humic acid raised total organic carbon by 21.4 grams per kilogram within 28 days. But the authors caution that these numbers cannot be pooled into a universal average, because responses depend on feedstock, production conditions, soil texture, mineralogy, pH, moisture, climate and experimental duration.</p>
<p>The most provocative part of the review concerns what a rise in soil carbon actually means for the climate. Soils globally release roughly 60 petagrams of carbon per year through decomposition, a gross flux that dwarfs annual fossil fuel emissions, though it is largely part of the natural carbon cycle. When an amendment is added, total carbon dioxide emissions may fall or rise, but a bulk flux measurement alone cannot tell scientists whether the carbon came from the amendment or from the soil&#8217;s native organic matter. The review draws a sharp evidentiary line: only isotope-based or otherwise source-resolved methods count as direct evidence of priming, the acceleration or suppression of native soil carbon decomposition. Many widely cited studies, it turns out, fall short of that standard.</p>
<p>Biochar studies report both positive and negative priming depending on pyrolysis conditions, soil pH and texture, substrate supply and duration. Hydrochar, with its soluble and aliphatic components, may boost short-term respiration, but the authors stress this is not proof of positive priming without source separation. Evidence for artificial humic substances remains thin, with few isotope-tracing studies. The message is blunt: no material class can be assumed to uniformly suppress native carbon loss, and short-term declines in carbon dioxide emissions may simply reflect transient microbial suppression or substrate limitation rather than genuine stabilization.</p>
<p>The mechanistic heart of the review organizes sequestration into three interacting pillars. The first is material persistence: pyrolysis creates condensed aromatic structures that resist decomposition, while hydrochar contains larger microbially accessible fractions, and artificial humic substances may gain persistence through association with minerals despite their chemical reactivity. Elemental ratios such as hydrogen-to-carbon and oxygen-to-carbon serve as rough screening tools, but the authors warn they cannot capture pore accessibility, mineral coatings or carbon-domain heterogeneity. Long-term isotope studies confirm that biochar contains persistent fractions while also releasing a measurable labile fraction shortly after incorporation, yet comparable multi-year field data for the other two classes are almost entirely absent.</p>
<p>The second pillar is physical and mineral protection. Soil aggregates restrict microbial access to carbon, and artificial carbon materials can promote aggregation through their pores, surface chemistry and interactions with clay minerals, roots, fungal hyphae and microbial glues. In grassland and rice paddy soils, biochar increased macroaggregates within the first 60 days, with microaggregates enriched in biochar-derived carbon developing later. Mineral type matters enormously: expanding 2:1 clays like montmorillonite offer far more sorption capacity than kaolinite, and iron and aluminum oxides can lock up carboxyl-rich compounds through ligand exchange and co-precipitation. Aging further reshapes these interfaces, with mineral bonding detected on biochar after roughly three months and organo-mineral coatings observed on particles recovered from field trials after up to 9.5 years.</p>
<p>The third pillar is microbial transformation. Artificial carbon materials modify habitat conditions, buffering water fluctuations and altering pH, nutrients and redox, while their soluble compounds feed microbes. Rather than simply sitting inert, amendment carbon can flow through microbial biomass into necromass, the dead residues that subsequently bind to minerals or become sealed inside aggregates. A 12-year field experiment found biochar increased microbial necromass carbon by 23.3 to 39.0 percent in topsoil but reduced it at depth, while a four-year paddy study reported decreases at all depths measured, a reminder that total soil carbon gains can coexist with losses in specific microbial carbon pools. Microspectroscopic work in a long-term pasture showed biochar particles sorbing root-derived carbon and accumulating mineral coatings that incorporated microbial necromass, effectively lifting the soil&#8217;s carbon ceiling.</p>
<p>The review&#8217;s practical upshot is that there is no universally optimal material. Alkaline biochars suit acidic soils but risk over-liming neutral ones; hydrochar fits wet wastes that need no pre-drying but carries soluble carbon whose fate varies; artificial humic substances offer reactive mineral interactions and may even promote biological carbon dioxide assimilation, though their long-term field persistence is unproven. The authors call for multi-year, multi-site trials using isotope source partitioning, standardized aging protocols, integrated mineralogical and microbial analyses, and full life-cycle assessments. As the 4 per mille initiative seeks to grow global soil carbon stocks by 0.4 percent annually, this review offers both a caution and a roadmap: engineered carbon materials can genuinely help soils fight climate change, but only if scientists and farmers track where the carbon comes from, where it goes, and how long it stays.</p>
<p><strong>Subject of Research:</strong> Mechanisms of soil organic carbon sequestration by artificial carbon materials in agroecosystems</p>
<p><strong>Article Title:</strong> Artificial carbon materials for soil organic carbon sequestration in agroecosystems: A bibliometric analysis and mechanistic review</p>
<p><strong>Article References:</strong> Xu, P., Yu, H., Zhang, J., Xu, Y., &amp; Liu, Z. (2026). Artificial carbon materials for soil organic carbon sequestration in agroecosystems: A bibliometric analysis and mechanistic review. <em>Journal of Agriculture and Food Research, 31</em>, Article 103343. <a href="https://doi.org/10.1016/j.jafr.2026.103343" rel="noopener noreferrer">https://doi.org/10.1016/j.jafr.2026.103343</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.1016/j.jafr.2026.103343" rel="noopener noreferrer">10.1016/j.jafr.2026.103343</a></p>
<p><strong>Keywords:</strong> soil organic carbon, biochar, hydrochar, artificial humic substances, carbon sequestration, priming effect, soil aggregates, mineral association, microbial necromass, greenhouse gas emissions, agroecosystems, climate change mitigation</p>
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		<post-id xmlns="com-wordpress:feed-additions:1">231734</post-id>	</item>
		<item>
		<title>Water-Saving Irrigation and Hydrochar Reshape Carbon Storage in Paddy Soil Clumps</title>
		<link>https://scienmag.com/water-saving-irrigation-and-hydrochar-reshape-carbon-storage-in-paddy-soil-clumps/</link>
		
		<dc:creator><![CDATA[Alan Morgan]]></dc:creator>
		<pubDate>Wed, 23 Sep 2026 23:40:57 +0000</pubDate>
				<category><![CDATA[Agriculture]]></category>
		<category><![CDATA[aggregate stability]]></category>
		<category><![CDATA[carbon cycling in flooded rice paddies]]></category>
		<category><![CDATA[carbon sequestration]]></category>
		<category><![CDATA[combined irrigation and organic amendments in agriculture]]></category>
		<category><![CDATA[controlled irrigation]]></category>
		<category><![CDATA[controlled irrigation in rice cultivation]]></category>
		<category><![CDATA[effects of irrigation regime on soil organic matter]]></category>
		<category><![CDATA[hydrochar]]></category>
		<category><![CDATA[hydrochar soil amendment]]></category>
		<category><![CDATA[hydrothermal carbonization]]></category>
		<category><![CDATA[impact of hydrochar on soil microbial communities]]></category>
		<category><![CDATA[microbial biomass]]></category>
		<category><![CDATA[organic carbon sequestration in paddy soils]]></category>
		<category><![CDATA[paddy soil]]></category>
		<category><![CDATA[rice straw]]></category>
		<category><![CDATA[soil aggregate structure and carbon storage]]></category>
		<category><![CDATA[soil aggregates]]></category>
		<category><![CDATA[soil organic carbon]]></category>
		<category><![CDATA[soil physics and organic carbon retention]]></category>
		<category><![CDATA[soil pore architecture and carbon dynamics]]></category>
		<category><![CDATA[soil structure]]></category>
		<category><![CDATA[sustainable rice farming methods]]></category>
		<category><![CDATA[water-saving irrigation]]></category>
		<category><![CDATA[water-saving irrigation practices]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=211290</guid>

					<description><![CDATA[A controlled experiment shows that switching flooded rice paddies to water-saving irrigation and amending soil with straw-derived hydrochar shifts the size distribution of soil aggregates and locks more organic carbon into large, stable clumps.]]></description>
										<content:encoded><![CDATA[<p>Beneath every flooded rice paddy lies an architecture most people never think about: a three-dimensional labyrinth of soil crumbs, ranging from grit-like microaggregates to chunky clumps visible to the naked eye. How those crumbs are sized, how tightly they hold together, and how much organic carbon they trap inside their pores may sound like arcane soil physics, but it sits at the heart of two of agriculture&#8217;s biggest challenges: keeping water in the fields where rice is grown and keeping carbon out of the atmosphere. A new study published in Plant and Soil by Kechun Wang of Northwest A&amp;F University and Hohai University, together with colleagues at Ghent University and collaborators in China, shows that two management choices — switching from continuous flooding to controlled irrigation, and amending soil with a charcoal-like material called hydrochar — can measurably reorganize this hidden architecture and shift where organic carbon accumulates within it.</p>
<p>The team&#8217;s starting point was a gap in the literature. The link between soil aggregates and soil organic carbon cycling has been documented extensively, yet the combined effects of irrigation regime and exogenous organic carbon additions on aggregate distribution, aggregate-bound carbon and microbial communities in paddy soils remained poorly understood. Paddy soils are an unusual case: they spend much of the growing season saturated, which changes everything from oxygen availability to how particles stick together. As water-saving irrigation schemes spread across rice-growing regions to conserve scarce freshwater, researchers have worried about what drier, more fluctuating moisture conditions do to the physical structures that protect carbon in these soils. The new experiment was designed to answer that question directly.</p>
<p>Methodologically, the study was deliberately gentle with its samples. Rather than subjecting soil to aggressive dry sieving, which can shatter natural aggregates and distort the size distribution, the researchers used an optimal-moisture sieving method, working the soil at a moisture content chosen to preserve aggregate integrity. Soil was separated into size classes, from large aggregates larger than 2 millimeters down to fine fractions smaller than 0.25 millimeters. The treatments compared flooding irrigation with controlled irrigation, and each water regime was crossed with additions of rice straw or with hydrochar produced from that same straw by hydrothermal carbonization — a process that converts wet biomass into a carbon-rich, chemically altered solid using heat and pressure in water.</p>
<p>The first striking result is how lopsided paddy soil architecture turned out to be. Across the treatments, aggregates larger than 2 millimeters dominated the soil mass, accounting for between 67 and 80 percent of the total, while the finest fraction below 0.25 millimeters was the least abundant class at just 7 to 16 percent. That imbalance matters more than it might seem. When scientists calculate how much organic carbon sits in the soil as a whole, the bulk of the number comes from whatever size class holds most of the mass — in this case, the big aggregates — even if smaller fractions are individually richer in carbon per gram. The study confirmed exactly this pattern: the fine fractions were enriched in organic carbon and microbial attributes, yet the larger-than-2-millimeter class made the largest numerical contribution to calculated bulk soil organic carbon simply because of its overwhelming mass proportion.</p>
<p>Water management left a clear fingerprint on this architecture. Compared with continuous flooding, controlled irrigation increased the proportion of large aggregates greater than 2 millimeters and improved aggregate-related structural indices, as reflected in higher values of mean weight diameter and geometric mean diameter — two standard measures that essentially summarize whether a soil is dominated by sturdy, well-formed crumbs or by loose, easily eroded fragments. For a water-saving technique, that is a reassuring outcome. It suggests that the drying and re-wetting cycles inherent to controlled irrigation do not necessarily degrade paddy soil structure; instead, under the conditions of this experiment, they appear to have nudged the soil toward a coarser, better-aggregated state.</p>
<p>Adding exogenous organic carbon raised the amount of organic carbon associated with aggregates in both water regimes, but the two amendments behaved in intriguingly different ways. Rice straw proved the stronger stimulator of microbial biomass, consistent with its role as a fresh, easily decomposable food source for soil organisms. Hydrochar, by contrast, produced a greater increase in the proportion of large aggregates and in the organic carbon concentration within that greater-than-2-millimeter class. In other words, straw fed the microbes, while hydrochar built the structure — and locked more carbon into the biggest, mass-dominant crumbs. The authors conclude that hydrochar amendment under controlled irrigation improved aggregate-related structural characteristics and increased aggregate-associated organic carbon mainly by boosting both the mass share and the carbon concentration of the large-aggregate fraction.</p>
<p>The interaction between the two levers was not simply additive. The study found that controlled irrigation and hydrochar amendment influenced aggregate distribution and aggregate-associated organic carbon independently and, for some aggregate-size responses, interactively. This nuance carries practical weight: it means farmers and researchers cannot assume that the effect of a soil amendment is the same under a flooded field as under a water-saving schedule. The moisture regime sets a context that shapes how organic additions translate into physical structure and carbon stabilization, which is precisely the kind of information needed to design management packages rather than isolated interventions.</p>
<p>Why should carbon cling to large aggregates so effectively when hydrochar enters the picture? The mechanistic story, as the authors and the surrounding literature frame it, involves the way particulate organic materials act as binding agents. Fresh plant residues serve as nuclei around which mineral particles and microbial products accumulate, forming larger and more stable aggregates. Hydrochar, being more chemically recalcitrant than raw straw, persists longer and may act as a durable skeletal component within these crumbs, while its own carbon rides along inside the aggregate structure. Meanwhile, the enrichment of organic carbon and microbial attributes in the fine fractions reflects the reality that microaggregates offer protected microhabitats where decomposers and their substrates are held in close, moisture-buffered contact. Both ends of the size spectrum do important work — they just do it in different currencies.</p>
<p>For rice systems, which cover vast areas of Asia and store substantial carbon in their periodically waterlogged soils, the findings arrive at a moment when water scarcity is pushing irrigation reform and carbon accounting is tightening around agriculture. Controlled irrigation is already valued for cutting water use and, according to related work by overlapping research groups, for mitigating methane emissions from paddies. This study adds a structural dimension to its credentials: the practice did not sacrifice, and in fact improved, the aggregation metrics that underpin soil physical health. Pairing it with hydrochar made from the very straw that rice harvests generate offers a circular route — crop residue is converted off-field and returned as a stable carbon amendment that reinforces soil structure rather than decomposing rapidly and releasing its carbon back to the air.</p>
<p>Cautions remain, as they always do with short-term experiments. The aggregates and microbial responses reported here were measured under experimental conditions, and longer-term field studies will be needed to confirm that hydrochar-driven gains in large-aggregate carbon persist across seasons and soil types, and that microbial stimulation by straw does not simply accelerate carbon loss elsewhere in the system. The researchers also note that datasets from the study are available from the corresponding author on reasonable request, inviting replication. Still, the central message is crisp and actionable: the amount of carbon a paddy soil can bank depends not just on what you add to it, but on how wet you keep it — and the best results come when the two are tuned together.</p>
<p><strong>Subject of Research:</strong> Effects of controlled irrigation and hydrochar amendment on soil aggregate-size distribution and aggregate-associated organic carbon in paddy soils</p>
<p><strong>Article Title:</strong> Controlled irrigation and hydrocchar amendment alter aggregate-size distribution and aggregate-associated organic carbon in paddy soils</p>
<p><strong>Article References:</strong> Controlled irrigation and hydrocchar amendment alter aggregate-size distribution and aggregate-associated organic carbon in paddy soils. (n.d.). <a href="https://doi.org/10.1007/s11104-026-09144-9" rel="noopener noreferrer">https://doi.org/10.1007/s11104-026-09144-9</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.1007/s11104-026-09144-9" rel="noopener noreferrer">10.1007/s11104-026-09144-9</a></p>
<p><strong>Keywords:</strong> paddy soil, soil aggregates, hydrochar, controlled irrigation, soil organic carbon, rice straw, microbial biomass, aggregate stability, carbon sequestration, water-saving irrigation, soil structure, hydrothermal carbonization</p>
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		<post-id xmlns="com-wordpress:feed-additions:1">211290</post-id>	</item>
		<item>
		<title>Moderate Biochar Rates Unlock Higher Vegetable Yields and Nitrogen Efficiency in Southern China</title>
		<link>https://scienmag.com/moderate-biochar-rates-unlock-higher-vegetable-yields-and-nitrogen-efficiency-in-southern-china/</link>
		
		<dc:creator><![CDATA[Alan Morgan]]></dc:creator>
		<pubDate>Sun, 20 Sep 2026 23:20:22 +0000</pubDate>
				<category><![CDATA[Earth Science]]></category>
		<category><![CDATA[Biochar]]></category>
		<category><![CDATA[Biochar application in vegetable farming]]></category>
		<category><![CDATA[Calibration of biochar application rates]]></category>
		<category><![CDATA[Environmental impact of fertilizer overuse]]></category>
		<category><![CDATA[greenhouse gas emissions from agriculture]]></category>
		<category><![CDATA[Guangdong Province]]></category>
		<category><![CDATA[intensive farming]]></category>
		<category><![CDATA[Intensive vegetable cropping systems]]></category>
		<category><![CDATA[microbial biomass]]></category>
		<category><![CDATA[Nitrogen leaching reduction techniques]]></category>
		<category><![CDATA[nitrogen use efficiency]]></category>
		<category><![CDATA[Nitrogen use efficiency in Chinese agriculture]]></category>
		<category><![CDATA[nutrient availability]]></category>
		<category><![CDATA[Rice straw biochar benefits]]></category>
		<category><![CDATA[rice straw pyrolysis]]></category>
		<category><![CDATA[soil aggregates]]></category>
		<category><![CDATA[soil amendments]]></category>
		<category><![CDATA[Soil health restoration methods]]></category>
		<category><![CDATA[soil quality]]></category>
		<category><![CDATA[sustainable agriculture]]></category>
		<category><![CDATA[sustainable soil management practices]]></category>
		<category><![CDATA[Urban market vegetable production]]></category>
		<category><![CDATA[vegetable crop yield improvement]]></category>
		<category><![CDATA[vegetable production]]></category>
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					<description><![CDATA[A two-year field experiment in Guangdong Province found that applying 20 tons of rice-straw biochar per hectare increased vegetable yields, nitrogen use efficiency, and soil quality, while higher rates offered no additional benefit.]]></description>
										<content:encoded><![CDATA[<p>Intensive vegetable farming in Southern China is famous for its remarkable productivity, supplying bustling urban markets with leafy greens grown in rapid, near-continuous rotations. Yet behind those impressive harvests lies a stubborn problem that has plagued agricultural scientists for decades: farmers apply enormous quantities of nitrogen fertilizer, but only a fraction of that nutrient ever reaches the crop. The rest is lost to leaching, volatilization, and microbial transformations, polluting waterways, releasing greenhouse gases, and wasting money. Now, a two-year field experiment conducted in Guangdong Province offers compelling evidence that a single, carefully calibrated intervention—biochar made from rice straw—can simultaneously raise yields, tighten nitrogen cycling, and rebuild degraded soil health. Crucially, the study shows that the dose makes the medicine, with a moderate application of 20 metric tons per hectare outperforming both no amendment and heavier treatments.</p>
<p>The research, published in the journal Nitrogen Cycling, was carried out by a team led by Zonghai Chen and corresponding author Bo Li of South China Agricultural University, together with colleagues including Yige Liu, Jiashuai Hu, Ying Lu, and Lars Elsgaard. The investigators set up an intensive vegetable field planted with lettuce varieties, a cropping system typical of the humid subtropical conditions that dominate much of Southern China&#8217;s vegetable belt. Five biochar application rates were compared, spanning from zero as a control up to 40 metric tons per hectare, all under conventional nitrogen fertilization. The biochar itself was produced from rice straw, an abundant agricultural residue, through pyrolysis at 500 degrees Celsius, a thermal conversion process that locks carbon and mineral nutrients into a porous, charcoal-like material prized for its ability to alter soil physical and chemical properties.</p>
<p>The results were striking. Over the two-year experiment, the 20-ton-per-hectare treatment increased vegetable yields by 10 to 29 percent compared with plots that received no biochar. Nitrogen use efficiency, the proportion of applied fertilizer nitrogen actually captured by the crop, improved by 18 to 160 percent, a range that reflects year-to-year variability but consistently favors the moderate dose. Plant nitrogen uptake rose by 14 to 33 percent, meaning the lettuce not only grew larger but also accumulated more of the nutrient that drives leafy growth. In a sector where nitrogen use efficiency often languishes well below 40 percent, gains of this magnitude represent a meaningful step toward both economic and environmental sustainability, reducing the fertilizer inputs farmers must purchase while cutting the nutrient losses that degrade rivers and groundwater across the region.</p>
<p>What happens underground proved just as important as what happens above it. Biochar transformed the physical architecture of the soil, promoting the formation and stability of water-resistant aggregates—the small, crumb-like structures that give healthy soils their spongy texture, allowing them to hold moisture during dry spells yet drain freely after heavy rains. This aggregate stability matters enormously in Guangdong&#8217;s climate, where intense monsoonal downpours can sluice nutrients out of poorly structured soils. The amendment also increased microbial biomass, swelling the populations of bacteria and fungi that mediate decomposition, nutrient mineralization, and nitrogen transformations. At the optimal rate, the researchers&#8217; composite soil quality index climbed 39.7 percent above the control in the first year and 50.6 percent higher in the second year, indicating that the benefits were not a fleeting first-season flush but a persistent improvement that actually strengthened with time.</p>
<p>To understand how these soil changes translated into better crops, the team employed statistical modeling that traced the pathways linking biochar to plant performance. Their analysis indicated that biochar influenced vegetable production and nitrogen utilization largely through three interlocking channels: altered soil nutrient availability, shifts in microbial communities, and improved soil structure. Higher soil quality scores were positively associated with vegetable yield, nitrogen uptake, and nitrogen use efficiency, suggesting a coherent causal chain in which the amendment acts first on the soil environment and only subsequently on the plant. This mechanistic clarity is valuable because it distinguishes biochar from a simple fertilizer substitute. Rather than directly feeding the crop, the material appears to function as a soil ecosystem engineer, creating conditions under which native nutrient cycles and microbial processes operate more effectively in partnership with conventional fertilization.</p>
<p>Perhaps the most consequential finding, however, is what did not happen at high application rates. The response of vegetable yield and nitrogen-related indicators was decidedly non-linear, rising steadily as biochar application climbed toward roughly 20 tons per hectare and then declining beyond that threshold. Plots amended with 30 or 40 tons per hectare showed no additional yield benefit, and the researchers caution that excessive rates could disturb nutrient balance or disrupt microbial conditions. In other acidic or nutrient-poor soils, very high biochar doses can immobilize nitrogen, raise pH beyond optimal ranges for some crops, or dilute mineral nutrient concentrations in ways that undermine rather than enhance fertility. The message for practitioners is unambiguous: more biochar is not necessarily better, and the amendment behaves as a dose-responsive tool rather than a cure-all to be applied liberally.</p>
<p>The dose-response relationship also carries significant economic weight. Biochar is not free; producing, transporting, and incorporating tens of tons of material per hectare represents a substantial investment, particularly for smallholder vegetable growers operating on thin margins. When the research team weighed crop benefits against biochar costs under the conditions of their experiment, 20 tons per hectare emerged as the most favorable amendment rate, delivering the strongest combination of yield gains, nitrogen savings, and soil improvement per unit of material applied. This kind of cost-benefit framing is essential if biochar is to move from research plots into the fields of working farms. An intervention that performs brilliantly in a scientific trial but fails an economic test will remain a curiosity; one that pays for itself through higher yields and reduced fertilizer waste has a realistic path to adoption.</p>
<p>Bo Li, the corresponding author, emphasized this balanced perspective in discussing the findings. According to the study team, a moderate application rate provided the best balance between improving soil conditions, supporting soil microorganisms, and helping vegetable crops use nitrogen more efficiently. That framing captures a broader shift in soil science away from viewing amendments as single-purpose inputs and toward managing them as components of an integrated system. In the Guangdong experiment, biochar did not replace nitrogen fertilizer; it made conventional fertilization more effective by reshaping the soil matrix in which nutrient transformations occur. For policymakers and extension services promoting low-carbon agriculture, this synergy matters, because biochar also sequesters carbon in a stable form, meaning a practice that boosts farm profitability may simultaneously contribute to climate mitigation.</p>
<p>The authors are careful to note the limits of their evidence. The experiment spanned only two years, a short window in the life of a soil system, and longer-term studies will be needed to determine how long the observed benefits persist and whether repeated moderate applications are required in warm, high-rainfall regions where biochar may decompose faster and nutrients cycle rapidly. Tropical and subtropical conditions can accelerate the aging of biochar particles, potentially altering their effects on nutrient retention over time. Questions also remain about how the optimal rate might shift across different soil types, crops, and management regimes beyond the lettuce rotations studied here. Still, the consistency of the improvements across two growing seasons, the strong mechanistic support linking soil quality to crop performance, and the clear identification of a cost-effective optimum give the findings practical credibility.</p>
<p>Taken together, the study positions carefully optimized biochar application as a realistic route toward more productive, nitrogen-efficient intensive vegetable farming in Southern China and potentially in comparable systems worldwide. By pinpointing 20 tons per hectare as the sweet spot, the research converts a broad enthusiasm for soil amendments into an actionable prescription, one that acknowledges the economics of farming and the complexity of soil ecology in equal measure. As demands on intensive vegetable systems continue to grow alongside the region&#8217;s population, strategies that squeeze more food from every kilogram of applied nitrogen—while restoring the structural and biological foundations of the soil itself—will only become more valuable. This experiment suggests that, with the right dose, rice straw that once might have been burned or discarded can become a cornerstone of that effort.</p>
<p><strong>Subject of Research:</strong> Effects of rice-straw biochar application rates on vegetable yields, nitrogen use efficiency, and soil quality in intensive vegetable fields in Southern China</p>
<p><strong>Article Title:</strong> Right dose of biochar boosts vegetable yields and nitrogen efficiency in Southern China</p>
<p><strong>Article References:</strong> Right dose of biochar boosts vegetable yields and nitrogen efficiency in Southern China. (n.d.). <a href="https://www.eurekalert.org/news-releases/1144469" 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> biochar, nitrogen use efficiency, vegetable production, soil quality, soil aggregates, microbial biomass, rice straw pyrolysis, intensive farming, Guangdong Province, soil amendments, nutrient availability, sustainable agriculture</p>
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