<?xml version="1.0" encoding="UTF-8"?><rss version="2.0"
	xmlns:content="http://purl.org/rss/1.0/modules/content/"
	xmlns:wfw="http://wellformedweb.org/CommentAPI/"
	xmlns:dc="http://purl.org/dc/elements/1.1/"
	xmlns:atom="http://www.w3.org/2005/Atom"
	xmlns:sy="http://purl.org/rss/1.0/modules/syndication/"
	xmlns:slash="http://purl.org/rss/1.0/modules/slash/"
	>

<channel>
	<title>grassland conservation &#8211; Science</title>
	<atom:link href="https://scienmag.com/tag/grassland-conservation/feed/" rel="self" type="application/rss+xml" />
	<link>https://scienmag.com</link>
	<description></description>
	<lastBuildDate>Fri, 02 Oct 2026 05:05:01 +0000</lastBuildDate>
	<language>en-US</language>
	<sy:updatePeriod>
	hourly	</sy:updatePeriod>
	<sy:updateFrequency>
	1	</sy:updateFrequency>
	<generator>https://wordpress.org/?v=7.1.2</generator>

<image>
	<url>https://scienmag.com/wp-content/uploads/2024/07/cropped-scienmag_ico-32x32.jpg</url>
	<title>grassland conservation &#8211; Science</title>
	<link>https://scienmag.com</link>
	<width>32</width>
	<height>32</height>
</image> 
<site xmlns="com-wordpress:feed-additions:1">73899611</site>	<item>
		<title>Planting Trees on Farmland, Not Grassland, Unlocks China&#8217;s Soil Carbon Bonanza</title>
		<link>https://scienmag.com/planting-trees-on-farmland-not-grassland-unlocks-chinas-soil-carbon-bonanza/</link>
		
		<dc:creator><![CDATA[Sloane Callahan]]></dc:creator>
		<pubDate>Fri, 02 Oct 2026 05:05:01 +0000</pubDate>
				<category><![CDATA[Agriculture]]></category>
		<category><![CDATA[afforestation]]></category>
		<category><![CDATA[carbon saturation]]></category>
		<category><![CDATA[carbon sequestration]]></category>
		<category><![CDATA[carbon sequestration in former croplands]]></category>
		<category><![CDATA[China]]></category>
		<category><![CDATA[China's afforestation and climate change]]></category>
		<category><![CDATA[Climate Mitigation]]></category>
		<category><![CDATA[climate mitigation through tree planting]]></category>
		<category><![CDATA[cropland restoration]]></category>
		<category><![CDATA[effectiveness of nature-based climate actions]]></category>
		<category><![CDATA[grassland conservation]]></category>
		<category><![CDATA[land use change]]></category>
		<category><![CDATA[long-term soil carbon dynamics]]></category>
		<category><![CDATA[Machine learning]]></category>
		<category><![CDATA[natural grassland conversion to forest]]></category>
		<category><![CDATA[nature-based solutions]]></category>
		<category><![CDATA[optimizing tree planting for climate benefits]]></category>
		<category><![CDATA[Plant and Soil]]></category>
		<category><![CDATA[reforestation impact on soil carbon]]></category>
		<category><![CDATA[soil carbon monitoring and analysis]]></category>
		<category><![CDATA[soil carbon saturation principles]]></category>
		<category><![CDATA[soil organic carbon]]></category>
		<category><![CDATA[soil organic carbon storage]]></category>
		<category><![CDATA[soil texture and mineralogy influence]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=225830</guid>

					<description><![CDATA[A synthesis of 361 afforestation sites across China shows that planting trees on former cropland delivers decades of sustained soil carbon gains, while converting natural grasslands to forests yields none, pointing to carbon-poor lands as the smartest targets for climate-focused planting.]]></description>
										<content:encoded><![CDATA[<p>China has planted more trees than any other nation on Earth, a greening campaign visible from orbit and celebrated as a flagship of nature-based climate action. But a new analysis of 361 afforestation sites across the country delivers an uncomfortable and fascinating twist: where those trees were planted matters enormously for the climate ledger. Converting natural grasslands into forests, the study finds, produced no significant gain in soil organic carbon storage at all, and showed no sustained accumulation over decades of monitoring. Former croplands, by contrast, responded dramatically, with soil carbon gains that persisted for more than sixty years after the trees went in. The research, published in the journal Plant and Soil by a team led by Fangyan Zhang and Yiping Wu of Xi&#8217;an Jiaotong University, suggests that one of the world&#8217;s largest carbon offsetting experiments may have been quietly misallocating effort, and that a simple principle, target carbon-poor soils, could multiply the climate payoff of future planting.</p>
<p>The science behind this divergence comes down to a concept that soil scientists call carbon saturation. Soils do not absorb organic carbon without limit; each soil has a finite capacity, governed largely by its texture, mineralogy and structure, to bind organic molecules onto mineral surfaces and lock them inside stable aggregates. Natural grasslands, which have accumulated organic matter continuously for centuries or millennia through dense, deep root systems and slow decomposition, tend to sit close to that ceiling. Their baseline soil organic carbon stocks are already high. When a forest is established on such land, the new trees add litter and root inputs, but the soil simply has little remaining capacity to stash the additional carbon in stable forms. The result, documented across the study&#8217;s grassland-to-forest sites, is a statistical flat line: neither significant storage gains nor a meaningful upward trend through time.</p>
<p>Former croplands tell the opposite story. Decades of tillage, harvest removal and fallow exposure strip agricultural soils of much of their organic matter, oxidizing it into carbon dioxide and breaking down the aggregates that would otherwise protect it. When cultivation stops and trees take over, that depleted soil behaves like an empty sponge. Root exudates, leaf litter and the slow rain of dead microbial biomass begin rebuilding the organic pool, and because the starting point is so low, nearly every gram of new carbon represents a genuine net gain for the atmosphere-to-land flux. The study found that the largest soil carbon gains occurred precisely in soils with the lowest initial carbon content, a pattern the authors interpret as evidence that the stronger response of former croplands reflects their greater capacity for carbon recovery after long-term cultivation.</p>
<p>To reach these conclusions, the researchers assembled one of the most comprehensive field datasets yet compiled for Chinese afforestation, integrating observations from 361 sites spanning the country&#8217;s major planting regions and land-use histories. Rather than relying on a single metric, they quantified long-term changes in soil organic carbon storage and then used statistical modeling, including machine learning approaches such as random forests, to disentangle the drivers behind the divergent trajectories. The chronosequence design, comparing sites of different ages since planting, allowed the team to reconstruct temporal dynamics that no single snapshot could capture, revealing that cropland afforestation sustains accumulation for at least six decades while grassland conversion shows no such persistent trend.</p>
<p>The most consequential part of the analysis is spatial. The team scaled their findings across China at a one-kilometer resolution, asking a deliberately policy-relevant question: what happens to national soil carbon storage if afforestation is targeted at carbon-poor lands under an optimized zonation strategy? Their answer was striking. Under such targeting, the national average soil organic carbon stock could rise by 30 percent within ten years and by 79 percent after sixty years. Those figures are not a forecast of what will happen under current practice; they are an upper bound of what optimized siting could achieve, and the gap between the two is precisely where the climate value of smarter land-use planning lies.</p>
<p>The findings land in the middle of a lively international debate about the true climate value of tree planting. Large-scale forestation pledges have proliferated worldwide, but a series of recent studies has warned that planting trees in drylands, on peatlands, or in naturally open ecosystems can fail to deliver promised carbon benefits, sometimes even reducing surface albedo and increasing warming. Earlier meta-analyses, including work on northern European afforestation and global land-use change, have reported similarly mixed results depending on prior land cover, soil type and climate. What the new Chinese dataset adds is scale and temporal depth: hundreds of sites, decades of post-planting history, and a direct comparison of the two most common afforestation pathways, cropland conversion and grassland conversion, within a single analytical framework.</p>
<p>The mechanistic picture also connects to broader theory about how carbon becomes stable in soil. Organic matter enters soil through plant litter and root deposits, is processed by microbial communities, and is ultimately stabilized either through chemical association with silt and clay particles or through physical occlusion inside aggregates. Soils far from saturation have abundant free mineral surfaces and unoccupied protective niches, so a large fraction of incoming carbon is retained. Near-saturated soils, like mature grasslands, have fewer such vacancies, and much of the new input simply cycles back to the atmosphere through microbial respiration. This framework, often described through carbon saturation concepts in the literature, predicts exactly the asymmetry the study observed, and it implies that the same logic should apply beyond China&#8217;s borders wherever afforestation programs are being sited.</p>
<p>There is an important conservation message embedded in the results as well. The finding that grassland afforestation yields no significant soil carbon gain does not merely mean such projects are inefficient; it means they may sacrifice something valuable for nothing. Grasslands are themselves major carbon reservoirs, storing much of their carbon belowground in roots and stable soil fractions, and they support distinctive biodiversity and pastoral livelihoods. Plowing or planting over them to create forests risks disturbing existing stocks, potentially releasing carbon that took centuries to accumulate, while delivering no compensating sequestration. The authors explicitly call for land-use-sensitive afforestation strategies that conserve existing grassland carbon stocks while directing planting toward carbon-poor lands with the greatest recovery potential.</p>
<p>For policymakers, the practical recipe is unusually clear. Inventories of soil carbon, increasingly produced with machine learning models trained on field observations and remote sensing data, can identify the depleted, carbon-poor landscapes, degraded farmland above all, where every planted hectare buys the most sequestration. China&#8217;s own massive programs, from the Grain for Green initiative on the Loess Plateau to shelterbelt plantations across the north, offer both the laboratory and the test case, and the new upscaling results suggest that a modest shift in siting rules could transform their climate accounting. As nations race to meet net-zero pledges with nature-based solutions, the lesson from 361 Chinese field sites is deceptively simple: the climate benefit of a tree depends as much on the soil it stands in as on the tree itself, and the biggest carbon wins are waiting in the ground we have already emptied.</p>
<p><strong>Subject of Research:</strong> Soil organic carbon sequestration following afforestation of croplands and grasslands in China</p>
<p><strong>Article Title:</strong> Divergent soil carbon gains from cropland and grassland afforestation in China</p>
<p><strong>Article References:</strong> Zhang, F., Meng, Z., Wu, Y., Wang, P., Tu, Y., An, S., Yin, X., Zhang, G., &amp; Zhen, H. (2026). Divergent soil carbon gains from cropland and grassland afforestation in China. <em>Plant and Soil</em>. <a href="https://doi.org/10.1007/s11104-026-09155-6" rel="noopener noreferrer">https://doi.org/10.1007/s11104-026-09155-6</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.1007/s11104-026-09155-6" rel="noopener noreferrer">10.1007/s11104-026-09155-6</a></p>
<p><strong>Keywords:</strong> afforestation, soil organic carbon, carbon sequestration, grassland conservation, cropland restoration, China, climate mitigation, carbon saturation, nature-based solutions, land-use change, machine learning, Plant and Soil</p>
]]></content:encoded>
					
		
		
		<post-id xmlns="com-wordpress:feed-additions:1">225830</post-id>	</item>
		<item>
		<title>Mapping Assam’s Wild Edible Herb Reveals Hidden Grassland Conservation Hotspots</title>
		<link>https://scienmag.com/mapping-assams-wild-edible-herb-reveals-hidden-grassland-conservation-hotspots/</link>
		
		<dc:creator><![CDATA[Margaret Porter]]></dc:creator>
		<pubDate>Sat, 29 Aug 2026 03:07:15 +0000</pubDate>
				<category><![CDATA[Climate]]></category>
		<category><![CDATA[Assam]]></category>
		<category><![CDATA[Assam grassland conservation]]></category>
		<category><![CDATA[community conservation]]></category>
		<category><![CDATA[community-based conservation Assam]]></category>
		<category><![CDATA[distribution]]></category>
		<category><![CDATA[grassland conservation]]></category>
		<category><![CDATA[grassland ecosystem preservation]]></category>
		<category><![CDATA[grassland-woodland ecotones India]]></category>
		<category><![CDATA[habitat restoration for medicinal plants]]></category>
		<category><![CDATA[herbacea]]></category>
		<category><![CDATA[impact of rainfall patterns on grassland species]]></category>
		<category><![CDATA[MaxEnt modeling]]></category>
		<category><![CDATA[non-timber forest products]]></category>
		<category><![CDATA[Northeast India biodiversity hotspots]]></category>
		<category><![CDATA[plant distribution ecological modeling]]></category>
		<category><![CDATA[Predicting]]></category>
		<category><![CDATA[Premna]]></category>
		<category><![CDATA[Premna herbacea]]></category>
		<category><![CDATA[Premna herbacea habitat modeling]]></category>
		<category><![CDATA[species distribution]]></category>
		<category><![CDATA[threatened wildlife Assam national parks]]></category>
		<category><![CDATA[traditional edible herbs Assam]]></category>
		<category><![CDATA[traditional medicinal plants Assam]]></category>
		<category><![CDATA[wild edible plants]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=184383</guid>

					<description><![CDATA[A MaxEnt model identifies 1,331 square kilometres of potential habitat for Assam’s culturally important wild edible herb, with key strongholds in Manas and Orang National Parks.]]></description>
										<content:encoded><![CDATA[<p>A plant gathered for generations as food and traditional medicine has now become the subject of Assam’s first detailed ecological distribution model. Researchers have mapped the potential habitat of <i>Premna herbacea</i> Roxb., a perennial herb of the mint family that grows along the grassland–woodland ecotones of northeastern India. Their analysis suggests that the species occupies a far narrower landscape than its cultural importance might imply: approximately 1,331 square kilometres of Assam is currently suitable for it. Much of that area lies in the sub-Himalayan grasslands of Manas and Orang National Parks, ecosystems that also support some of South Asia’s most threatened wildlife. The findings transform scattered plant records into a conservation map, identifying both protected strongholds and possible restoration areas beyond park boundaries. The study, led by researchers including Soumitra Goswami, Moloya Gogoi, Jonmani Kalita and Manisha Choudhury, argues that conserving the plant will require more than protecting isolated populations. It will require maintaining the grassland processes, seasonal rainfall patterns, soils and community practices that allow the species to persist.</p>
<p>Known as <i>Kheraidaphni</i> among the Bodo community and <i>Matiajam</i> more broadly in Assam, <i>P. herbacea</i> is harvested as a leafy vegetable and used in traditional medicine. Young shoots, leaves and ripe fruits are consumed, and earlier nutritional studies have reported approximately 15.38 percent protein and 41.75 percent carbohydrates, along with micronutrients including zinc, molybdenum, copper, manganese, iron and magnesium. The plant also contains reported phytochemicals such as phenolics, flavonoids, terpenoids and saponins. Traditional systems including Ayurveda, Siddha and Unani have associated the species with treatments for diabetes, jaundice, fever and sleeping sickness, while laboratory research has begun investigating possible antioxidant, antidiabetic and liver-related effects. Those uses do not by themselves establish clinical efficacy, but they illustrate why the plant is important to local communities. Its recognition as a Geographical Indication and its status as a non-timber forest product add economic and cultural value, while harvesting pressure creates a practical conservation challenge: the same plant can be both a livelihood resource and a vulnerable component of a shrinking habitat.</p>
<p>To estimate where the herb could occur, the researchers used Maximum Entropy, or MaxEnt, version 3.4.4, a species-distribution algorithm designed to work with presence-only observations. Such models do not require researchers to document every place where a species is absent. Instead, they compare known occurrence locations with environmental conditions across a study region and estimate how suitable other locations may be. The team assembled 75 georeferenced records from field surveys, published studies, herbarium material and ethnobotanical databases. Because clusters of records can make a model learn the geography of surveying rather than the ecology of a species, the researchers applied spatial thinning. They removed records located within one kilometre of one another and ensured that no two observations occupied the same 30-arcsecond grid cell, leaving 65 records for modelling. This procedure reduced the effects of spatial autocorrelation and helped limit overfitting, although it could not eliminate geographic sampling bias entirely.</p>
<p>The analysis covered Assam, a state of about 78,438 square kilometres extending from the Eastern Himalaya toward the Indo-Burman ranges. The region includes the Brahmaputra and Barak river valleys, alluvial floodplains, wetlands, riparian woodland, moist deciduous forest and sub-Himalayan grasslands. Elevation ranges from roughly 15 metres above sea level in the floodplains to more than 1,800 metres in foothills and uplands. Assam’s subtropical monsoonal climate delivers about 1,807 millimetres of annual rainfall, with more than 70 percent arriving during the June-to-September monsoon. From 19 bioclimatic variables, elevation-related layers, soil information and land-use data, the researchers retained nine predictors after correlation and variance-inflation screening. The final variables represented temperature patterns, annual and seasonal precipitation, elevation, soil type and land use or land cover. Pairwise correlations above 0.80 were removed, and the remaining variables were screened using a variance inflation factor threshold of three, reducing the risk that overlapping predictors would distort the model.</p>
<p>The resulting model showed exceptionally strong discrimination across its evaluation measures. Ten bootstrap replicates produced a mean area under the receiver operating characteristic curve of 0.995, with a standard deviation of 0.003. The true skill statistic was 0.87 and Cohen’s kappa was 0.84. AUC measures how effectively a model ranks suitable sites above unsuitable ones, while TSS and kappa assess classification performance using sensitivity and specificity, with kappa also correcting for agreement expected by chance. The researchers optimized model complexity with the ENMeval package, testing regularization settings and feature combinations through spatially partitioned cross-validation. The selected configuration used a regularization multiplier of 1.5 and linear-plus-hinge features, with 10,000 background points and 10 bootstrap runs. The prediction was expressed in cloglog format, producing suitability values from zero to one. Strong metrics indicate a well-performing model for the available data, but they do not mean that every predicted site contains the plant or that the species’ future range is guaranteed.</p>
<p>Of the estimated 1,331 square kilometres of suitable habitat, 383 square kilometres, or 28.79 percent, was classified as highly suitable. Another 199 square kilometres, or 14.95 percent, fell into the moderate category, while 749 square kilometres, or 56.26 percent, was designated low suitability. The classifications were based on the maximum training sensitivity plus specificity threshold, a method intended to balance missed presences against false-positive predictions in presence-only modelling. The strongest concentration appeared across the northern sub-Himalayan grassland belt, especially in and around Manas and Orang National Parks. Within those protected areas, the model identified 810 square kilometres of suitable habitat: 354 square kilometres of high suitability, 89 square kilometres of moderate suitability and 367 square kilometres of low suitability. High-suitability habitat therefore represented 43.70 percent of suitable area inside the parks, compared with 28.79 percent across Assam as a whole. The result highlights the parks as important refuges, while also showing that a substantial portion of the potential range lies outside their core boundaries.</p>
<p>Land use and land cover emerged as the most influential predictor, contributing 59.0 percent to the model and accounting for 53.9 percent of permutation importance. Suitability was highest in grassland classes and declined sharply in agricultural, forest and built-up areas. Precipitation seasonality, represented by the bioclimatic variable BIO15, contributed 21.7 percent and had the same value for permutation importance, showing that the timing and variability of rainfall are central to the plant’s distribution. Assam’s monsoon cycle influences grassland growth, soil moisture and the timing of conditions suitable for establishment. Soil type was also identified as a major driver, likely because substrate properties affect water retention and nutrient availability. Elevation contributed 5.3 percent, yet its permutation importance reached 12.8 percent, suggesting that small topographic differences may influence local moisture and soil conditions. Jackknife tests supported the importance of land cover and precipitation seasonality: each produced high model gain when used alone and caused the greatest reduction in gain when omitted.</p>
<p>These patterns place the plant’s conservation within the broader crisis facing tropical and subtropical grasslands. Such habitats are increasingly altered by woody encroachment, invasive alien plants, changes in fire regimes, agriculture and other human pressures. The loss or conversion of open grassland can remove suitable conditions for <i>P. herbacea</i> even when the surrounding landscape remains green. The species’ predicted range also overlaps habitats used by the pygmy hog, greater one-horned rhinoceros and Bengal florican, making management decisions relevant to several conservation priorities at once. Harvesting inside protected areas may create additional disturbance, while poorly regulated collection could reduce local plant populations. At the same time, excluding communities from management would overlook the knowledge, food value and income linked to the species. Because suitable areas were predicted in buffer and peripheral zones, the researchers propose ecological restoration and community-based or co-managed harvesting as possible strategies. Such measures could include protecting grassland structure, monitoring populations, regulating collection and linking conservation rules with equitable local benefits.</p>
<p>The study is a first spatial assessment rather than a final range map. Its occurrence records were concentrated in Manas and Orang, where survey effort has been comparatively strong, so the model may overrepresent protected-area conditions. The analysis also describes suitability under current environmental conditions and does not project how future climate change could alter rainfall seasonality, temperature or habitat availability. Independent field surveys across high-, moderate- and low-suitability areas would provide a stronger test of the predictions and could reveal undocumented populations. Even with those uncertainties, the map supplies a practical framework for deciding where surveys, restoration and harvest monitoring should begin. The central message is that a culturally valued edible herb depends on a specialized and threatened grassland landscape. Protecting <i>P. herbacea</i> will therefore require coordinated action among communities, forest managers and conservation planners, combining habitat protection with sustainable use. By connecting local food traditions to quantitative habitat modelling, the research gives Assam a more precise basis for conserving both the plant and the grasslands that sustain it.</p>
<p><strong>Subject of Research:</strong> Potential habitat and conservation needs of Premna herbacea in Assam</p>
<p><strong>Article Title:</strong> Predicting the distribution of Premna herbacea Roxb., a wild edible plant from the plains of Assam</p>
<p><strong>Article References:</strong> Goswami, S., Gogoi, M., Kalita, J., &amp; Choudhury, M. (2026). Predicting the distribution of Premna herbacea Roxb., a wild edible plant from the plains of Assam. <em>Discover Conservation, 3</em>(1), Article 36. <a href="https://doi.org/10.1007/s44353-026-00105-y" rel="noopener noreferrer">https://doi.org/10.1007/s44353-026-00105-y</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.1007/s44353-026-00105-y" rel="noopener noreferrer">10.1007/s44353-026-00105-y</a></p>
<p><strong>Keywords:</strong> Premna herbacea, Assam, MaxEnt modeling, species distribution, grassland conservation, wild edible plants, non-timber forest products, community conservation, Predicting, distribution, Premna, herbacea</p>
]]></content:encoded>
					
		
		
		<post-id xmlns="com-wordpress:feed-additions:1">184383</post-id>	</item>
	</channel>
</rss>
