<?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>peatland rewetting &#8211; Science</title>
	<atom:link href="https://scienmag.com/tag/peatland-rewetting/feed/" rel="self" type="application/rss+xml" />
	<link>https://scienmag.com</link>
	<description></description>
	<lastBuildDate>Fri, 02 Oct 2026 13:56:18 +0000</lastBuildDate>
	<language>en-US</language>
	<sy:updatePeriod>
	hourly	</sy:updatePeriod>
	<sy:updateFrequency>
	1	</sy:updateFrequency>
	<generator>https://wordpress.org/?v=7.1.3</generator>

<image>
	<url>https://scienmag.com/wp-content/uploads/2024/07/cropped-scienmag_ico-32x32.jpg</url>
	<title>peatland rewetting &#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>How Restored Soils Lock Away Carbon: The Hidden Machinery Beneath Our Feet</title>
		<link>https://scienmag.com/how-restored-soils-lock-away-carbon-the-hidden-machinery-beneath-our-feet/</link>
		
		<dc:creator><![CDATA[Sloane Callahan]]></dc:creator>
		<pubDate>Fri, 02 Oct 2026 13:56:18 +0000</pubDate>
				<category><![CDATA[Agriculture]]></category>
		<category><![CDATA[afforestation]]></category>
		<category><![CDATA[agroforestry]]></category>
		<category><![CDATA[carbon sequestration]]></category>
		<category><![CDATA[Climate Mitigation]]></category>
		<category><![CDATA[degraded land recovery]]></category>
		<category><![CDATA[ecosystem restoration for carbon storage]]></category>
		<category><![CDATA[effects of deforestation on soil carbon]]></category>
		<category><![CDATA[global land degradation and carbon loss]]></category>
		<category><![CDATA[grazing exclusion]]></category>
		<category><![CDATA[impact of land degradation on greenhouse gases]]></category>
		<category><![CDATA[Land degradation]]></category>
		<category><![CDATA[land restoration]]></category>
		<category><![CDATA[land restoration and climate mitigation]]></category>
		<category><![CDATA[organic carbon stabilization mechanisms]]></category>
		<category><![CDATA[organo-mineral associations]]></category>
		<category><![CDATA[peatland rewetting]]></category>
		<category><![CDATA[peatland rewetting and carbon capture]]></category>
		<category><![CDATA[soil aggregate and mineral functions in climate change]]></category>
		<category><![CDATA[soil aggregation]]></category>
		<category><![CDATA[soil carbon sequestration]]></category>
		<category><![CDATA[soil microbial role in carbon storage]]></category>
		<category><![CDATA[soil microbiome]]></category>
		<category><![CDATA[soil mineralization processes]]></category>
		<category><![CDATA[soil organic carbon]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=228111</guid>

					<description><![CDATA[A sweeping systematic review of 25 years of research reveals that soil aggregates, mineral associations and microbial communities, not just the plants above ground, determine whether ecosystem restoration truly locks away carbon for the long term.]]></description>
										<content:encoded><![CDATA[<p>Beneath every replanted forest, rewetted peatland and fenced-off grassland lies a hidden engine of climate mitigation, and a new systematic review has now mapped its gears in unprecedented detail. The study, published in Discover Soil, synthesizes a quarter century of global research on how land restoration reshapes the physical, chemical and biological machinery of soil to accumulate and stabilize organic carbon. Its central message is striking: the climate value of restoration is not decided by the trees we can see, but by the aggregates, minerals and microbes we cannot. Roughly 35 million square kilometers of land, about 24 percent of Earth&#8217;s land surface, is already degraded, and the review argues that understanding soil processes is the key to turning that liability back into a carbon sink.</p>
<p>The scale of the problem the review confronts is enormous. Land degradation, driven by unsustainable agriculture, deforestation, overgrazing and urban expansion, strips ecosystems of their capacity to store carbon and actively releases it. The authors report that approximately one third of the 78 plus or minus 12 gigatonnes of carbon lost through soil organic carbon depletion is attributable to soil degradation and erosion, with the remaining two thirds arising from mineralization of organic matter. Water and wind erosion alone strip an estimated 1.3 and 1.0 petagrams of carbon per year from soils globally, and cumulative carbon dioxide emissions from eroded soils have been found to rise by 56 percent in transport zones and 27 percent in depositional zones. Deforestation and forest degradation together contribute roughly a quarter of global emissions, with deforestation alone emitting about 6.22 gigatonnes of carbon dioxide annually.</p>
<p>To build their synthesis, the researchers searched the Web of Science database for literature published between January 2000 and December 2024, using combinations of terms covering land degradation, restoration practices and carbon sequestration. Following PRISMA screening protocols, the dataset was refined from thousands of records down to 2,178 peer-reviewed English-language articles. Bibliometric tools including Biblioshiny and VOSviewer revealed a field in rapid expansion: annual output grew from just 19 articles in 2000 to 205 in 2024, an annual growth rate of 10.42 percent, with international co-authorship appearing in 36.72 percent of publications. China dominated the research landscape with 2,052 publications, followed by the United States with 618 and India with 386, while keyword clustering showed the field shifting from early concerns with erosion and soil degradation toward remote sensing, alpine meadows and soil organic carbon dynamics.</p>
<p>The review then catalogues how different restoration interventions translate into measurable carbon gains, and the numbers are often dramatic. In West Java, Indonesia, high-density mixed-species agroforestry systems sequestered up to 108.9 megagrams of carbon per hectare while simultaneously reducing erosion. In Northeast India, Piper betel and rubber plantations captured 4.94 and 3.92 megagrams of carbon per hectare per year respectively. China&#8217;s Returning Grazing Land to Grassland program increased soil organic carbon by 0.27 megagrams per hectare per year, and in Ethiopia, grazing exclosures lifted soil carbon stocks from 52 to 76 tonnes per hectare over just ten years. Vegetative barriers of Stylosanthes scabra and Vetiveria zizanoides in contour trenching raised surface soil carbon stocks by more than 110 percent, while restored mangroves in Southeast India sequestered nearly ten thousand times more carbon per hectare per year than adjacent degraded stands.</p>
<p>Yet the most technically compelling section of the review concerns the mechanisms that make these gains durable rather than transient. When vegetation returns, litter inputs and root biomass increase, feeding organic matter into the soil and fueling the formation of stable aggregates, clumps of mineral particles bound by root exudates and microbial products that physically shield carbon from decomposers. In karst rocky desertification areas of China, afforestation increased aggregate-associated soil organic carbon by 7.89 to 26.96 grams per kilogram, with larger macroaggregates showing the strongest correlation with carbon stabilization. Mean weight diameter of aggregates rose 1.65-fold and geometric mean diameter 2.76-fold in afforested topsoil compared with cultivated land. Meanwhile, organo-mineral associations, in which organic compounds bind to iron and aluminum oxides, provide a second stabilization pathway that can lock carbon away for decades.</p>
<p>The review documents equally profound changes in soil physical properties. In China&#8217;s Danangou watershed, bulk density initially increased during the first decade after afforestation but then declined significantly over 20 to 40 years as root development and organic matter accumulation restored porosity. In the Tianhe Watershed of Shaanxi Province, average bulk density in the top 60 centimeters fell from 1.73 grams per cubic centimeter in saline wasteland to 1.45 grams per cubic centimeter under mixed forests. Soil texture itself shifted over time: sand content in the topsoil decreased while silt and clay fractions increased two to three decades after planting, improving aggregate stability, microbial activity and nutrient retention. These changes enhance water infiltration and reduce surface runoff, creating a self-reinforcing loop in which better soil structure supports more biomass, which in turn builds more structure.</p>
<p>Microbial communities emerge as a third pillar of restoration-driven carbon dynamics. In degraded karst regions, afforestation with natural forests significantly increased the abundance of beneficial microbial taxa such as Rhizobiales and Methylomirabilota, which participate in nitrogen fixation and organic carbon cycling, and this rise in microbial activity correlated positively with carbon stored within soil aggregates. In Caofeidian, China, broadleaved afforestation improved soil bacterial diversity by 27.2 percent in surface soil and 15.7 percent in deeper layers. The review emphasizes that microbial processing of organic carbon is not simply a matter of decomposition; microbes also produce the binding agents and residual carbon compounds that underpin long-term stabilization, making the soil microbiome both a gatekeeper and an architect of sequestration.</p>
<p>Crucially, the authors resist the temptation to declare restoration a universal win. The magnitude and even the direction of soil carbon responses depend strongly on ecosystem context, restoration age, soil mineralogy and hydrological conditions. Afforestation in Mediterranean Spain improved net ecosystem production to 112 grams of carbon per square meter per year, but the denser vegetation increased transpiration and reduced water yield, a carbon-water trade-off with serious implications for water-limited regions. Afforestation with Robinia pseudoacacia on the Loess Plateau raised soil carbon stocks by 18.60 to 25.75 percent depending on stand age, but induced soil acidification through organic matter decomposition and root exudates. Moderate acidification can actually aid stabilization by promoting organo-mineral binding, yet excessive acidification may disrupt microbial communities and nutrient cycling. In wetlands, water-table fluctuations govern the balance between carbon sequestration and methane emissions, adding another layer of complexity.</p>
<p>Timing and management intensity also matter enormously. Early-stage restoration typically shows rapid carbon accumulation driven by vegetation recovery, whereas long-term stabilization depends on the slower development of aggregates and mineral-associated organic carbon. Active planting dramatically accelerates the timeline: planted riparian forests in arid environments reached carbon stock maturity in 14 to 15 years, compared with 38 to 49 years for unplanted forests. Extended forest harvest cycles in Tibet increased aboveground biomass by 31 tonnes per hectare, and peatland rewetting, which halts aerobic peat oxidation, could save an estimated 1.91 gigatonnes of carbon dioxide every year globally. Even fire regimes play a nuanced role, with moderate fire belts supporting shrub biomass of 15.71 tonnes per hectare and sequestration rates of 1.57 tonnes per hectare per year, roughly double the rate of fire-free areas.</p>
<p>The review&#8217;s ultimate contribution is a decision framework linking specific degradation contexts to appropriate restoration strategies and their associated soil processes, from terracing and reforestation on erosion-prone slopes to hydrological management in coastal wetlands. The authors acknowledge limitations, including linguistic bias toward English-language sources and the difficulty of comparing studies with heterogeneous methods, but their synthesis makes a persuasive case that restoration policy must be soil-literate. As nations race toward the Paris Agreement targets and the United Nations Sustainable Development Goals, the review warns that maximizing climate mitigation requires site-adapted management, long-term monitoring and tools such as remote sensing and geospatial analysis. The carbon we hope to bury for centuries will only stay buried if the aggregates, minerals and microbes beneath the surface are given the conditions they need to do their quiet, essential work.</p>
<p><strong>Subject of Research:</strong> Soil processes regulating organic carbon accumulation and stabilization in restored ecosystems</p>
<p><strong>Article Title:</strong> Restoration-driven soil processes regulating organic carbon accumulation and stabilization in restored ecosystems</p>
<p><strong>Article References:</strong> Roy, J., Dutta, S., Sarkar, S., Gorain, S., &amp; Banerjee, K. (2026). Restoration-driven soil processes regulating organic carbon accumulation and stabilization in restored ecosystems. <em>Discover Soil, 3</em>(1), Article 132. <a href="https://doi.org/10.1007/s44378-026-00289-8" rel="noopener noreferrer">https://doi.org/10.1007/s44378-026-00289-8</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.1007/s44378-026-00289-8" rel="noopener noreferrer">10.1007/s44378-026-00289-8</a></p>
<p><strong>Keywords:</strong> soil organic carbon, land restoration, carbon sequestration, soil aggregation, afforestation, peatland rewetting, soil microbiome, organo-mineral associations, land degradation, agroforestry, grazing exclusion, climate mitigation</p>
]]></content:encoded>
					
		
		
		<post-id xmlns="com-wordpress:feed-additions:1">228111</post-id>	</item>
		<item>
		<title>Peatland Rewetting Reshapes Mosquito Communities in Unexpected Ways, Study Finds</title>
		<link>https://scienmag.com/peatland-rewetting-reshapes-mosquito-communities-in-unexpected-ways-study-finds/</link>
		
		<dc:creator><![CDATA[Margaret Porter]]></dc:creator>
		<pubDate>Wed, 23 Sep 2026 22:30:40 +0000</pubDate>
				<category><![CDATA[Biology]]></category>
		<category><![CDATA[Anopheles algeriensis]]></category>
		<category><![CDATA[Anopheles claviger]]></category>
		<category><![CDATA[biodiversity effects of peatland rewetting]]></category>
		<category><![CDATA[climate change mitigation through peatland rewetting]]></category>
		<category><![CDATA[effects of habitat restoration on rare mosquito species]]></category>
		<category><![CDATA[European Anopheles mosquitoes in rewetting projects]]></category>
		<category><![CDATA[GLMM]]></category>
		<category><![CDATA[impacts of wetland restoration on disease vectors]]></category>
		<category><![CDATA[implications for wetland conservation and public health]]></category>
		<category><![CDATA[integrated wetland management for climate and health]]></category>
		<category><![CDATA[landscape ecology]]></category>
		<category><![CDATA[landscape structure influence on mosquito ecology]]></category>
		<category><![CDATA[mosquito community response to rewetting]]></category>
		<category><![CDATA[mosquito ecology]]></category>
		<category><![CDATA[niche segregation]]></category>
		<category><![CDATA[North-East Germany]]></category>
		<category><![CDATA[One Health]]></category>
		<category><![CDATA[Parasites & Vectors]]></category>
		<category><![CDATA[peatland restoration]]></category>
		<category><![CDATA[peatland rewetting]]></category>
		<category><![CDATA[role of wetlands in mosquito-borne disease transmission]]></category>
		<category><![CDATA[vector surveillance]]></category>
		<category><![CDATA[weather influences on mosquito populations]]></category>
		<category><![CDATA[weather interactions]]></category>
		<guid isPermaLink="false">https://scienmag.com/?p=210826</guid>

					<description><![CDATA[A two-year study in North-East German peatlands shows that Anopheles algeriensis thrives in rewetted bogs while Anopheles claviger clusters in settlements, with landscape and weather interacting to shape each species' abundance.]]></description>
										<content:encoded><![CDATA[<p>Restoring drained peatlands has become one of the most celebrated tools in the fight against climate change, prized for its ability to lock away carbon, revive rare biodiversity and cool the landscape. But any large-scale change to wet ecosystems inevitably reshuffles the species that live there, and some of those species bite. New research from a fen peatland landscape in North-East Germany now offers one of the most detailed pictures yet of how two widespread European Anopheles mosquitoes respond when the water returns, revealing that each species follows its own ecological script shaped by an intricate interplay between landscape structure and weather. The findings, published in the open-access journal Parasites &amp; Vectors, carry direct implications for how wetland restoration and mosquito-borne disease surveillance should be planned together rather than treated as separate policy problems.</p>
<p>The study, led by Patrick Gutjahr, Amelie Weber, Susanne Fischer and Mandy Schäfer of the Friedrich-Loeffler-Institut, together with ecologists from the Greifswald Mire Centre and the University of Greifswald, focused on two mosquito species with very different public profiles. Anopheles algeriensis, first described by Theobald in 1903, is a comparatively rare and poorly studied member of the European mosquito fauna, while Anopheles claviger sensu stricto, originally described by Meigen in 1804, is far more common and broadly distributed across European wetlands. Both species are considered to have vector potential, meaning they are capable of transmitting pathogens under certain conditions, yet their precise ecological niches, the particular combination of habitat features and climatic conditions under which each thrives, had remained poorly resolved. That gap in knowledge matters, because peatland rewetting is being scaled up across Europe as a cost-effective climate mitigation strategy, and decision-makers need to know which mosquitoes rewetted landscapes will favor.</p>
<p>To answer that question, the research team carried out an intensive field campaign across a fen peatland landscape in North-East Germany. Adult mosquitoes were sampled biweekly, once every two weeks, over two consecutive flight seasons at 15 sites. The sites were then classified into three habitat types based on key peatland characteristics: wet peatlands, where the water table had been restored or naturally remained high; drained peatlands, where ditches and land use had lowered the water table; and settlements, the human-inhabited areas embedded within the landscape. Trapped anophelines that did not belong to the notoriously difficult Anopheles maculipennis complex were identified morphologically and, where necessary, confirmed with molecular methods targeting standard genetic barcodes, including the mitochondrial cytochrome c oxidase subunit 1 gene and the nuclear internal transcribed spacer 2 region. This combination of classical taxonomy and DNA-based verification ensured that the two focal species were distinguished with confidence.</p>
<p>The numbers alone tell a striking story of niche segregation, the process by which closely related or ecologically similar species partition the environment to avoid direct competition. Over the course of the study, the team collected 278 individuals of Anopheles algeriensis and a much larger haul of 950 specimens of Anopheles claviger sensu stricto. The rare species and the common species, as the paper&#8217;s title frames them, were not distributed at random. Anopheles algeriensis showed significantly higher abundances in wet peatlands than in any other habitat type, marking it as a specialist of the very environments that rewetting projects are working to recreate. Anopheles claviger sensu stricto, by contrast, reached its highest abundances in settlements, suggesting that the human-dominated edges of these landscapes provide conditions the species finds particularly favorable.</p>
<p>Habitat type, however, was only half of the equation. The researchers then deployed generalised linear mixed models, a statistical framework well suited to count data with repeated measures and hierarchical structure, to test how weather variables modulated abundance in each habitat type. The models estimated incidence rate ratios, allowing the team to quantify how a change in temperature, humidity or precipitation shifts expected mosquito counts. Weather data came from the German Weather Service, the Deutscher Wetterdienst, which provided reliable meteorological measurements for the study region. The result was a set of species-specific responses in which the effect of each weather variable depended, sometimes dramatically, on the surrounding landscape.</p>
<p>For Anopheles algeriensis, mean temperature emerged as a consistent ally. Abundance rose with warmer conditions regardless of habitat type, meaning the temperature effect was independent of the landscape context. Mean relative humidity was also positively correlated with abundance, but here the strength of the relationship was modulated by habitat type, indicating that humid air benefits the species most in certain settings. Perhaps most intriguingly, cumulative precipitation showed a negative correlation with abundance, and the strength of that negative relationship varied across habitat types. A rain-loving intuition might suggest the opposite for a wetland mosquito, but the pattern makes ecological sense: adult female mosquitoes, which are what the traps captured, tend to be less active in heavy or persistent rain, and the larvae of this species are presumably already assured of standing water in peatland habitats, so rainfall adds little larval benefit while suppressing adult flight and trap catches.</p>
<p>Anopheles claviger sensu stricto painted an almost mirror-image picture, underscoring how distinct the two species&#8217; environmental niches truly are. In settlements, mean relative humidity was positively correlated with abundance, echoing the humid-air benefit seen in its rarer relative. In the peatland habitats, however, the humidity effect flipped and became negative, a reversal that points to genuinely different physiological or behavioral tolerances between the species, or to different microhabitat preferences that make the same weather variable matter in opposite ways depending on where the mosquitoes live. Temperature effects were equally context-dependent: minimum temperature during trap nights was positively associated with abundance both in settlements and in wet peatlands, yet negatively associated in drained peatlands. A cooler night, in other words, can boost catches in one part of the landscape while depressing them in another.</p>
<p>These interaction effects, where landscape and weather jointly determine abundance, are the analytical heart of the study and the reason its findings go beyond a simple habitat checklist. In disease ecology, knowing that a vector species responds positively to warmth is useful, but knowing that the same warm spell multiplies its numbers in villages while doing the opposite in restored bogs is far more actionable. It means that surveillance efforts can be targeted spatially and temporally: trap networks and public health warnings can be concentrated in settlement habitats during warm, humid periods when Anopheles claviger sensu stricto is expected to peak, while wet peatland sites can be monitored for Anopheles algeriensis, whose populations climb with temperature across the board. The modeling approach, based on generalised linear mixed models with habitat type and weather interactions, provides a template that can be transferred to other rewetting landscapes across temperate Europe.</p>
<p>The broader context of this work is the CuliMoor project, funded by the German Federal Ministry of Research, Technology and Space, which examines the consequences of peatland rewetting within a One Health framework, the recognition that human, animal and ecosystem health are inseparably linked. Peatlands that remain drained continue to oxidize and release greenhouse gases, and rewetting them is among the most cost-effective climate actions available. Yet rewetting also changes the water table, vegetation structure and standing-water dynamics that mosquito larvae depend on. The new results demonstrate that such changes do not simply produce more mosquitoes or fewer mosquitoes; they shift the balance between species, potentially favoring different vectors in different parts of a restored landscape. As Gutjahr and colleagues put it in their conclusions, the species-specific responses to peatland habitat types highlight the need to integrate vector surveillance into rewetting and management strategies.</p>
<p>For now, the message from the North German fens is one of complexity and cautious optimism. Rewetted peatlands strongly favor Anopheles algeriensis, a species whose vector competence under natural conditions remains incompletely characterized, while the better-known Anopheles claviger sensu stricto concentrates in human settlements, where humidity and warm nights drive its numbers up. Neither pattern is inherently alarming, but both demand attention. The study&#8217;s authors emphasize that their findings were made possible by the many local volunteers who granted access to their plots and gardens and assisted with data collection, a reminder that large-scale ecological surveillance is as much a community endeavor as a technical one. As Europe accelerates its peatland restoration agenda, this work makes a compelling case that mosquito monitoring should ride along with the diggers and the hydrologists, ensuring that the climate benefits of returning water to the bogs are not achieved blind to their consequences for the tiny, buzzing inhabitants of the new wetlands.</p>
<p><strong>Subject of Research:</strong> Habitat suitability and niche segregation of two Anopheles mosquito species in North German peatlands</p>
<p><strong>Article Title:</strong> The rare and the common: habitat suitability and niche segregation of Anopheles algeriensis (Theobald, 1903) and Anopheles claviger s.s. (Meigen, 1804) in North-German peatlands is shaped by distinct landscape–weather interactions</p>
<p><strong>Article References:</strong> The rare and the common: habitat suitability and niche segregation of Anopheles algeriensis (Theobald, 1903) and Anopheles claviger s.s. (Meigen, 1804) in North-German peatlands is shaped by distinct landscape–weather interactions. (n.d.). <a href="https://doi.org/10.1186/s13071-026-07612-w" rel="noopener noreferrer">https://doi.org/10.1186/s13071-026-07612-w</a></p>
<p><strong>Image Credits:</strong> AI Generated</p>
<p><strong>DOI:</strong> <a href="https://doi.org/10.1186/s13071-026-07612-w" rel="noopener noreferrer">10.1186/s13071-026-07612-w</a></p>
<p><strong>Keywords:</strong> Anopheles algeriensis, Anopheles claviger, peatland rewetting, mosquito ecology, niche segregation, vector surveillance, North-East Germany, One Health, GLMM, landscape ecology, weather interactions, Parasites &amp; Vectors</p>
]]></content:encoded>
					
		
		
		<post-id xmlns="com-wordpress:feed-additions:1">210826</post-id>	</item>
	</channel>
</rss>
