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NL Institute of Ecology NIOO-KNAW

@niooknaw

The Netherlands Institute of Ecology (NIOO-KNAW) for biodiversity | climate change | sustainable use research. Academy institute. Spectacular sustainable building. www.nioo.knaw.nl

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Latest posts by NL Institute of Ecology NIOO-KNAW @niooknaw

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Medewerker Handopfok Vind jij het leuk om met dieren te werken en wil je (tijdelijk) jonge vogels verzorgen? Lees dan verder!

Vind jij het leuk om met dieren te werken en wil je (tijdelijk) jonge vogels verzorgen? Het werk bestaat uit het voeren van de jonge vogels en algemene dagelijkse schoonmaakwerkzaamheden, verwacht tussen 1 mei 2026 en 31 augustus 2026.

Reageer zo snel mogelijk: nioo.knaw.nl/nl/vacatures...

10.03.2026 11:51 👍 1 🔁 0 💬 0 📌 0
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Postdoc Development of a Microbial Volatile Database We are seeking a highly motivated postdoctoral researcher to develop and curate a comprehensive microbial volatile database within the framework of an interdisciplinary project at the Netherlands Inst...

Are you looking for a #postdoc that combines #bioinformatics with #microbial #ecology, metabolomics and data integration?
NIOO is seeking a highly motivated postdoctoral researcher to develop and curate a comprehensive microbial volatile #database.
Respond by 13 March: nioo.knaw.nl/en/vacancies...

09.03.2026 14:22 👍 3 🔁 5 💬 0 📌 0
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Symposium Evidence-based Rewilding & Launch Rewilding Expertise Centre What evidence shows that rewilding actually works? The symposium also marks the launch of the Rewilding Expertise Centre by NIOO researcher and special WUR professor Liesbeth Bakker on World Rewilding...

Hoe toon je aan dat #rewilding werkt? Kom erachter op 20 maart, bij het rewilding-symposium Evidence-based Rewilding.

Tijdens het #symposium lanceert ook het Rewilding Expertisecentrum. NIOO-onderzoekers Liesbeth Bakker en Nacho Villar leiden het symposium.

Meer info: nioo.knaw.nl/en/events/sy...

27.02.2026 10:23 👍 6 🔁 1 💬 0 📌 0
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Waarom krijgen dieren jonkies in de lente? De lammetjes dartelen in de wei en de vogels broeden op hun ei. De lente brengt niet alleen hogere temperaturen, maar verwelkomt ook een boel jonge diertjes. Waarom valt die geboortegolf precies in di...

Waarom krijgen dieren jonkies in de #lente?
‘Dieren timen hun voortplantingsgedrag op basis van het beschikbare voedsel’, vertelt NIOO-onderzoeker @keesvanoers.bsky.social aan Quest. In Nederland is het meeste eten er in het #voorjaar.
Lees het artikel: www.quest.nl/natuur/diere...

26.02.2026 11:29 👍 0 🔁 0 💬 0 📌 0
Figure 1 Stewart (2026): (a) Map of sampling locations in the Andean Mountain region of Ecuador. Samples were collected in either cultivated soils with either maize or potato crops, and in surrounding non-agricultural uncultivated vegetation. Samples were collected along a climate gradient covering 1600 m in elevation across a ~500 km transect. (b) Frequency distributions of mean annual precipitation (MAP, mm/m2) and mean annual temperature (MAT, °C) at the sampling locations, colour coded by crop type. (c) Samples were collected in a 10m2 grid with nine subsamples collected at and between each vertex, and a center point. Subsamples were then homogenised into one bulk sample. The image shows an example of a potato farm in the foreground and uncultivated vegetation in the background.

Figure 1 Stewart (2026): (a) Map of sampling locations in the Andean Mountain region of Ecuador. Samples were collected in either cultivated soils with either maize or potato crops, and in surrounding non-agricultural uncultivated vegetation. Samples were collected along a climate gradient covering 1600 m in elevation across a ~500 km transect. (b) Frequency distributions of mean annual precipitation (MAP, mm/m2) and mean annual temperature (MAT, °C) at the sampling locations, colour coded by crop type. (c) Samples were collected in a 10m2 grid with nine subsamples collected at and between each vertex, and a center point. Subsamples were then homogenised into one bulk sample. The image shows an example of a potato farm in the foreground and uncultivated vegetation in the background.

New publication: Land Use Change Reshapes #ClimateDriven Diversity Patterns of #Tropical Arbuscular #Mycorrhizal #Fungi. #landuse
doi.org/10.1111/mec....

23.02.2026 14:28 👍 0 🔁 0 💬 0 📌 0
Figure 2 Gouka (2026): Phylogenetic tree and inter-and intra-species variation of 96 wheat phyllosphere yeasts. (A) Maximum likelihood phylogeny based on 758 BUSCO single-copy genes of the whole yeast genomes. Genome statistics are shown for BUSCO, genome size (in Mb; orange), and GC content (in %; purple). Color stripes highlight low to higher values, ranging from light to dark color codes. (B) Heatmap of clustered log-transformed orthogroup gene counts. Yeast genera color coded based on taxonomy follows the same order as presented in the taxonomy legend. Stacked bar plot (right) indicates the number of orthogroups with gene counts.

Figure 2 Gouka (2026): Phylogenetic tree and inter-and intra-species variation of 96 wheat phyllosphere yeasts. (A) Maximum likelihood phylogeny based on 758 BUSCO single-copy genes of the whole yeast genomes. Genome statistics are shown for BUSCO, genome size (in Mb; orange), and GC content (in %; purple). Color stripes highlight low to higher values, ranging from light to dark color codes. (B) Heatmap of clustered log-transformed orthogroup gene counts. Yeast genera color coded based on taxonomy follows the same order as presented in the taxonomy legend. Stacked bar plot (right) indicates the number of orthogroups with gene counts.

New publication: #Genomic insights into #adaptative #traits of phyllosphere #yeasts by @lindagouka.bsky.social, @vivianecordovez.bsky.social and others.
doi.org/10.1186/s407...

23.02.2026 14:09 👍 0 🔁 0 💬 0 📌 0
Figure 6 Pei (2026): This conceptual model illustrates how applied biocontrol bacteria enhance pathogen inhibition by stimulating predatory protists, which subsequently increases the proportion of antibacterial genes. Pathway 1: Biocontrol bacteria stimulate the proliferation of predatory protists (Cercomonas). Under predation pressure, biocontrol bacteria (e.g., Bacillus) upregulate the production of disease-suppressive metabolites, which not only mediates their defense against protist grazing but also enhances the inhibition of pathogens (R. solanacearum). Pathway 2: Biocontrol bacteria directly secrete disease-suppressive metabolites to inhibit pathogens. The number of ‘+‘ and ‘-‘ signs indicates the significance of given effect.

Figure 6 Pei (2026): This conceptual model illustrates how applied biocontrol bacteria enhance pathogen inhibition by stimulating predatory protists, which subsequently increases the proportion of antibacterial genes. Pathway 1: Biocontrol bacteria stimulate the proliferation of predatory protists (Cercomonas). Under predation pressure, biocontrol bacteria (e.g., Bacillus) upregulate the production of disease-suppressive metabolites, which not only mediates their defense against protist grazing but also enhances the inhibition of pathogens (R. solanacearum). Pathway 2: Biocontrol bacteria directly secrete disease-suppressive metabolites to inhibit pathogens. The number of ‘+‘ and ‘-‘ signs indicates the significance of given effect.

New publication: #Biofertilizer induces #soil #disease suppression by activating #pathogen suppressive #protist taxa.
doi.org/10.1038/s415...

23.02.2026 13:01 👍 2 🔁 2 💬 1 📌 0
Graphical abstract Lammers (2026)

Graphical abstract Lammers (2026)

New publication: #Lipids as currency in #parasitoid competition: #Interactions between two #lipidscavenging species.
doi.org/10.1016/j.ji...

23.02.2026 12:56 👍 6 🔁 6 💬 0 📌 2
Figure 1 Charvalakis (2026): Boxplots showing the nightly number of captured insects per order per light colour, averaged across trap replicates. Other taxa (H) are Blattodea, Collembola, Psocoptera, and Trichoptera combined. Each boxplot represents the median, interquartile range, and spread of the data, while grey dots indicate the mean number of insects attracted per night. Bar plots in the top right corner of each panel represent the total catch per light colour across the entire sampling period. Plotted boxes sharing the same letter are not significantly different in terms of insect capture numbers (Tukey, α = 0.05).

Figure 1 Charvalakis (2026): Boxplots showing the nightly number of captured insects per order per light colour, averaged across trap replicates. Other taxa (H) are Blattodea, Collembola, Psocoptera, and Trichoptera combined. Each boxplot represents the median, interquartile range, and spread of the data, while grey dots indicate the mean number of insects attracted per night. Bar plots in the top right corner of each panel represent the total catch per light colour across the entire sampling period. Plotted boxes sharing the same letter are not significantly different in terms of insect capture numbers (Tukey, α = 0.05).

New publication: Timing of #attraction to #light of #nocturnal #insects is spectrum and taxon dependent: implications for mitigating #lightpollution, by @mevisser.bsky.social and others.
doi.org/10.1016/j.bi...

23.02.2026 11:24 👍 1 🔁 2 💬 0 📌 0
Figure 1 Van Leeuwen (2026): Conceptual view of the expected influence of the new littoral zones with recoupled habitats on primary producers, macroinvertebrate primary consumers and higher trophic levels in Lake Markermeer, The Netherlands. Primary production in the original lake in the pelagic zone (left food web) is mainly driven by pelagic phytoplankton. In the new littoral zones (right food web), additional contributions of benthic (macrophytes and periphyton) and terrestrial (shore plants) primary producers are expected, forming a broader base of consumers and higher trophic levels in a more complex food web. Food web based on Jin (2021).

Figure 1 Van Leeuwen (2026): Conceptual view of the expected influence of the new littoral zones with recoupled habitats on primary producers, macroinvertebrate primary consumers and higher trophic levels in Lake Markermeer, The Netherlands. Primary production in the original lake in the pelagic zone (left food web) is mainly driven by pelagic phytoplankton. In the new littoral zones (right food web), additional contributions of benthic (macrophytes and periphyton) and terrestrial (shore plants) primary producers are expected, forming a broader base of consumers and higher trophic levels in a more complex food web. Food web based on Jin (2021).

New publication: Recoupling #terrestrial, #benthic and #pelagic habitats by constructing #littoralzones diversifies #carbon flows to aquatic #macroinvertebrates.
doi.org/10.1016/j.ba...

23.02.2026 11:19 👍 2 🔁 1 💬 0 📌 0
Figure 1 Both (2026): (a) Correlation between the annual average hatching date and the date of the caterpillar peak (open dots are experimental years: 2015 (intermediate in caterpillar peak date of the three experimental years), 2021 (latest caterpillar peak date) and 2022 (earliest caterpillar peak date), (b) the interval between arrival and laying in response to the caterpillar peak, (c) the annual strength of selection on laying date, measured as the linear slope of standardized laying date on relative fitness (measured as the number of locally recruiting offspring per female) (open dots are experimental years: 2015, 2021 and 2022), (d) example of the correlation between individual interval between arrival and laying in response to variation in arrival date for two experimental years: blue triangles: 2021, a cold spring, and red dots: 2022, a relatively warm spring.

Figure 1 Both (2026): (a) Correlation between the annual average hatching date and the date of the caterpillar peak (open dots are experimental years: 2015 (intermediate in caterpillar peak date of the three experimental years), 2021 (latest caterpillar peak date) and 2022 (earliest caterpillar peak date), (b) the interval between arrival and laying in response to the caterpillar peak, (c) the annual strength of selection on laying date, measured as the linear slope of standardized laying date on relative fitness (measured as the number of locally recruiting offspring per female) (open dots are experimental years: 2015, 2021 and 2022), (d) example of the correlation between individual interval between arrival and laying in response to variation in arrival date for two experimental years: blue triangles: 2021, a cold spring, and red dots: 2022, a relatively warm spring.

New publication: Supplemental #feeding as #experimental #tool to understand why #birds do not #lay earlier in the #season, by @mevisser.bsky.social and others.
doi.org/10.1002/jav....

23.02.2026 11:14 👍 2 🔁 2 💬 0 📌 0
Figure 1 Ursem (2026) Map of camera trap locations, with (A) the location of the Marker Wadden study area in the Netherlands; (B) a detailed overview of the studied area of the Marker Wadden, with red triangles (n = 6) indicating the sampling locations and the black arrows indicating the direction of the camera traps and the transects. The blue circle shows the position of the water level data-logger. (C) Ground image of the setup of one of the camera traps, with the transects indicated by the sticks.

Figure 1 Ursem (2026) Map of camera trap locations, with (A) the location of the Marker Wadden study area in the Netherlands; (B) a detailed overview of the studied area of the Marker Wadden, with red triangles (n = 6) indicating the sampling locations and the black arrows indicating the direction of the camera traps and the transects. The blue circle shows the position of the water level data-logger. (C) Ground image of the setup of one of the camera traps, with the transects indicated by the sticks.

New publication: #Shorebird responses to fine-scale water level #fluctuations and #macrofauna biomass in a newly constructed #freshwater #wetland.
doi.org/10.1111/rec....

23.02.2026 11:10 👍 0 🔁 0 💬 0 📌 0
Figure 4 Bachtsevani (2026): Cyanate facilitating reciprocal cross-feeding at pH 6.0 between “Ca. Nitrobacter laanbroekii” NHB1 and N. devaniterrae Nd1 or N. sinensis Nd2. Cyanate was supplied at 0.05 mM (A) or 0.5 mΜ (B) as an NH+4 source. NH+4, NO−,2 and NO−3 concentrations were determined for all cultures and mean values and standard errors (mostly smaller than symbol size) from triplicate cultures are plotted. Decomposition of cyanate in the abiotic control produced <3.8 μM NH+4 during the period of incubation.

Figure 4 Bachtsevani (2026): Cyanate facilitating reciprocal cross-feeding at pH 6.0 between “Ca. Nitrobacter laanbroekii” NHB1 and N. devaniterrae Nd1 or N. sinensis Nd2. Cyanate was supplied at 0.05 mM (A) or 0.5 mΜ (B) as an NH+4 source. NH+4, NO−,2 and NO−3 concentrations were determined for all cultures and mean values and standard errors (mostly smaller than symbol size) from triplicate cultures are plotted. Decomposition of cyanate in the abiotic control produced <3.8 μM NH+4 during the period of incubation.

New publication: Acidotolerant #soil #nitriteoxidizer “Candidatus Nitrobacter laanbroekii” #NHB1 alleviates constraints on growth of acidophilic soil #ammoniaoxidizers.
doi.org/10.1093/isme...

23.02.2026 10:58 👍 1 🔁 1 💬 0 📌 0
Great tit, Branch, Feed image. Free for use. (jggrz, Pixabay, CC0)

Great tit, Branch, Feed image. Free for use. (jggrz, Pixabay, CC0)

New publication: Reactions of captive adult #greattits toward aposematic #prey: effects of #personality by @keesvanoers.bsky.social and others.
doi.org/10.1093/behe...

23.02.2026 10:48 👍 2 🔁 0 💬 0 📌 0
Graphical abstract Jacobusse (2026)

Graphical abstract Jacobusse (2026)

New publication: #Non-detection by citizen scientists modeled as a function of #visit characteristics. #citizenscientists
doi.org/10.1016/j.ec...

23.02.2026 10:23 👍 0 🔁 0 💬 0 📌 0
Firgure 1 Teitelbaum (2026): Locations and sampling intensity of tracked waterfowl during the breeding and winter seasons. Each 70-km grid cell shows the number of bird-days included in analyses at the 24-h observation scale. Map in Mollweide equal-area projection. Basemap of continental and national boundaries from Natural Earth.

Firgure 1 Teitelbaum (2026): Locations and sampling intensity of tracked waterfowl during the breeding and winter seasons. Each 70-km grid cell shows the number of bird-days included in analyses at the 24-h observation scale. Map in Mollweide equal-area projection. Basemap of continental and national boundaries from Natural Earth.

New publication: #Waterfowl Move Less in Heterogeneous and #HumanPopulated #Landscapes, With Implications for Spread of Avian #Influenza #Viruses.
doi.org/10.1111/ele.... #avianinfluenza

23.02.2026 10:19 👍 0 🔁 1 💬 0 📌 0
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Medewerker Facilitair Zoek jij een hele leuke startersfunctie in een internationale omgeving? Met een breed takenpakket, voldoende verantwoordelijkheid en opgewekte collega’s? Dan zijn wij op zoek naar jou!

Zoek jij een hele leuke startersfunctie als medewerker facilitair in een internationale omgeving? Met een breed takenpakket, voldoende verantwoordelijkheid en opgewekte collega’s? Dan zijn wij op zoek naar jou!

Lees verder via onze website: nioo.knaw.nl/nl/vacatures...

17.02.2026 13:40 👍 0 🔁 0 💬 0 📌 0
Figure 2 Radchuk (2026): A selection of studied species is shown, with each inset giving information for that species on its generation time (T, in years; also depicted by the black bar next to it), its diet (carnivore: C, herbivore: H, and omnivore: O) and whether the species is a migrant (M) or a resident (R). The inset shows the number of studies per taxon and trait category. Illustration credits for the species pictures taken from Wikipedia: Svalbard reindeer—Bjørn Christian Tørrissen, four-striped grass mouse—C.R. Selvakumar, silver gull—JJ Harrison, snow petrel—Samuel Blanc, northern giant petrel—Liam Quinn, green turtle—Brocken Inaglory, green-rumped parrotlet—Jam.mohd, Columbian ground squirrel—Martin Pot, red-winged fairy-wren—John Anderson, grey-headed albatross—John Harrison. Two species pictures were provided by the co-authors of this study: painted turtle (credit: FJ) and Atlantic yellow-nosed albatross (credit: SOp). The remaining pictures were taken from Pixabay (https://pixabay.com/photos/).

Figure 2 Radchuk (2026): A selection of studied species is shown, with each inset giving information for that species on its generation time (T, in years; also depicted by the black bar next to it), its diet (carnivore: C, herbivore: H, and omnivore: O) and whether the species is a migrant (M) or a resident (R). The inset shows the number of studies per taxon and trait category. Illustration credits for the species pictures taken from Wikipedia: Svalbard reindeer—Bjørn Christian Tørrissen, four-striped grass mouse—C.R. Selvakumar, silver gull—JJ Harrison, snow petrel—Samuel Blanc, northern giant petrel—Liam Quinn, green turtle—Brocken Inaglory, green-rumped parrotlet—Jam.mohd, Columbian ground squirrel—Martin Pot, red-winged fairy-wren—John Anderson, grey-headed albatross—John Harrison. Two species pictures were provided by the co-authors of this study: painted turtle (credit: FJ) and Atlantic yellow-nosed albatross (credit: SOp). The remaining pictures were taken from Pixabay (https://pixabay.com/photos/).

New publication: Changes in #phenology mediate #vertebrate #population responses to #temperature globally, by @stefanvriend.bsky.social, @mevisser.bsky.social, and others.
doi.org/10.1038/s414...

13.02.2026 11:53 👍 3 🔁 1 💬 0 📌 0
Figure 7 Zhou (2026): Conceptual diagram of the effects of grazing exclusion on the stocks of soil organic carbon fractions across two soil depths. Soil organic carbon (SOC) fractions include particulate organic carbon (POC) and mineral-associated organic carbon (MAOC). The percentage changes in SOC fractions represent the variations of the two grazing exclusion treatments relative to grazing across 0–30 cm soil depth. For the other predictor variables, the percentages represent the mean changes of the two grazing exclusion treatments relative to grazing, calculated separately for the 0–10 cm and 10–30 cm soil depths. Orange arrows denote positive effects, while blue arrows indicate negative effects. Ox:Hy ratios, oxidative-to-hydrolytic enzymes ratios.

Figure 7 Zhou (2026): Conceptual diagram of the effects of grazing exclusion on the stocks of soil organic carbon fractions across two soil depths. Soil organic carbon (SOC) fractions include particulate organic carbon (POC) and mineral-associated organic carbon (MAOC). The percentage changes in SOC fractions represent the variations of the two grazing exclusion treatments relative to grazing across 0–30 cm soil depth. For the other predictor variables, the percentages represent the mean changes of the two grazing exclusion treatments relative to grazing, calculated separately for the 0–10 cm and 10–30 cm soil depths. Orange arrows denote positive effects, while blue arrows indicate negative effects. Ox:Hy ratios, oxidative-to-hydrolytic enzymes ratios.

New publication: Contrasting responses of particulate and mineral-associated organic #carbon stocks to #grazing exclusion in an #alpine meadow.
doi.org/10.1016/j.ag...

13.02.2026 11:17 👍 0 🔁 0 💬 0 📌 0
Figure 1 Zhu (2026): Spatial distributions and migration corridors of Bohai Black-tailed Godwits during northward migration. Timing of migratory movements follows Zhu et al. (2021b). The dashed rectangle indicates the location of Bohai Bay. Drawings of Bohai Black-tailed Godwits by Seungha Oh. Hexagonal cells represent GPS telemetry locations collected between January-July, and darker shading indicates higher densities of recorded occurrences

Figure 1 Zhu (2026): Spatial distributions and migration corridors of Bohai Black-tailed Godwits during northward migration. Timing of migratory movements follows Zhu et al. (2021b). The dashed rectangle indicates the location of Bohai Bay. Drawings of Bohai Black-tailed Godwits by Seungha Oh. Hexagonal cells represent GPS telemetry locations collected between January-July, and darker shading indicates higher densities of recorded occurrences

New publication: Male and female Black-tailed #Godwits Limosa limosa bohaii show differences in #habitat use and daily #rhythms during #spring staging in #China. #Black-tailedGodwits #birds
doi.org/10.1007/s103...

13.02.2026 10:13 👍 10 🔁 3 💬 0 📌 0
Figure 1 Magnússon (2026): Experimental design and monitoring. Adapted after Magnússon et al. (2024). (a) Location of sites in the vicinity of Longyearbyen and Ny-Ålesund. Basemaps from www.toposvalbard.npolar.no. (b) At each site, we set out six or seven replicates per treatment, consisting of a Control (C) treatment and three Irrigation (I, ES, LS) treatments with different timing of rainfall events. (c) Each plot was a 4 m diameter circle, with fixed measurement points around the perimeter and in the centre, in which soil moisture (SM) was monitored. Vegetation composition, NDVI and vegetation height (VH) were measured in a smaller grid within the plot. Measurements of senescence and leaf sampling for specific leaf area (SLA) were carried out in the area in between the measurement points. (d) Timeline of the experiment and measurements in the plots around Longyearbyen. (e) Timeline of the experiment and measurements in the plots around Ny-Ålesund. For (d and e), Control and Irrigation (‘Legacy Experiment’) plots were set out in 2022, while Early-summer and Late-summer irrigation (‘Timing Experiment”) plots were added in 2023. Duration of plot monitoring is indicated by horizontal lines with colours corresponding to the treatments in (b). All plots were monitored until late summer 2024.

Figure 1 Magnússon (2026): Experimental design and monitoring. Adapted after Magnússon et al. (2024). (a) Location of sites in the vicinity of Longyearbyen and Ny-Ålesund. Basemaps from www.toposvalbard.npolar.no. (b) At each site, we set out six or seven replicates per treatment, consisting of a Control (C) treatment and three Irrigation (I, ES, LS) treatments with different timing of rainfall events. (c) Each plot was a 4 m diameter circle, with fixed measurement points around the perimeter and in the centre, in which soil moisture (SM) was monitored. Vegetation composition, NDVI and vegetation height (VH) were measured in a smaller grid within the plot. Measurements of senescence and leaf sampling for specific leaf area (SLA) were carried out in the area in between the measurement points. (d) Timeline of the experiment and measurements in the plots around Longyearbyen. (e) Timeline of the experiment and measurements in the plots around Ny-Ålesund. For (d and e), Control and Irrigation (‘Legacy Experiment’) plots were set out in 2022, while Early-summer and Late-summer irrigation (‘Timing Experiment”) plots were added in 2023. Duration of plot monitoring is indicated by horizontal lines with colours corresponding to the treatments in (b). All plots were monitored until late summer 2024.

New publication: #Seasonal timing and preceding #moisture regime mediate impacts of heavy #rainfall events on High #Arctic #plant growth.
doi.org/10.1111/1365...

13.02.2026 10:09 👍 0 🔁 0 💬 0 📌 0
Figure 1 O'Malley (2026): Yields varied substantially across the LegacyNet sites.
(A) The locations of the 26 LegacyNet sites, indicated by inverted yellow triangles (see data S1 for the site location details and ID codes). (B) The yield per growing season (t ha−1) based on plot-level measurements for each site are shown in boxplots that are grouped by mixtures (blue; 29 plots per site) and monocultures (gray; 18 plots per site), at the moderate nitrogen fertilizer level. The average yield of the six-species equiproportional mixture plots (three plots per site) is shown as a magenta triangle. The average yield of the monoculture plots from each functional group is highlighted with a circle (green for grass, orange for legume, and light blue for herb; six monoculture plots per functional group per site). The average yield of the high N grass monoculture (five plots per site) is shown by a red horizontal line. Sites are arranged on the x axis in order of decreasing median yield. The center line represents the median, box limits are upper and lower quartiles, and whiskers extend to the minimum and maximum of nonoutlier values.

Figure 1 O'Malley (2026): Yields varied substantially across the LegacyNet sites. (A) The locations of the 26 LegacyNet sites, indicated by inverted yellow triangles (see data S1 for the site location details and ID codes). (B) The yield per growing season (t ha−1) based on plot-level measurements for each site are shown in boxplots that are grouped by mixtures (blue; 29 plots per site) and monocultures (gray; 18 plots per site), at the moderate nitrogen fertilizer level. The average yield of the six-species equiproportional mixture plots (three plots per site) is shown as a magenta triangle. The average yield of the monoculture plots from each functional group is highlighted with a circle (green for grass, orange for legume, and light blue for herb; six monoculture plots per functional group per site). The average yield of the high N grass monoculture (five plots per site) is shown by a red horizontal line. Sites are arranged on the x axis in order of decreasing median yield. The center line represents the median, box limits are upper and lower quartiles, and whiskers extend to the minimum and maximum of nonoutlier values.

New publication: Multispecies #grasslands produce more #yield from lower #nitrogen inputs across a #climatic gradient.
doi.org/10.1126/scie...

12.02.2026 14:49 👍 2 🔁 0 💬 0 📌 0
Figure 3 Zagatto (2026): Microbial co-occurrence networks for hedgerows and fields and environmental correlations of network modules. (A) Microbial co-occurrence network from hedgerow soils. (B) Weighted R² contribution of environmental variables in explaining the structure of microbial co-occurrence modules in hedgerow network. The X-axis represents the weighted R² contribution of the significant variables. (C) Microbial co-occurrence network from field soils. (D) Weighted R² contribution of environmental variables in explaining the structure of microbial co-occurrence modules in field network. The X-axis represents the weighted R² contribution of the significant variables. Networks in (A) and (C) were constructed using SpiecEasi inference from ASVs of both fungi and prokaryotes. Nodes are represented by circles and indicate microbial taxa. Edges are represented by lines and indicated significant associations. Different node sizes represent the betweenness centrality.

Figure 3 Zagatto (2026): Microbial co-occurrence networks for hedgerows and fields and environmental correlations of network modules. (A) Microbial co-occurrence network from hedgerow soils. (B) Weighted R² contribution of environmental variables in explaining the structure of microbial co-occurrence modules in hedgerow network. The X-axis represents the weighted R² contribution of the significant variables. (C) Microbial co-occurrence network from field soils. (D) Weighted R² contribution of environmental variables in explaining the structure of microbial co-occurrence modules in field network. The X-axis represents the weighted R² contribution of the significant variables. Networks in (A) and (C) were constructed using SpiecEasi inference from ASVs of both fungi and prokaryotes. Nodes are represented by circles and indicate microbial taxa. Edges are represented by lines and indicated significant associations. Different node sizes represent the betweenness centrality.

New publication: Land use influences #prokaryotes more than #fungi in adjacent #hedgerow soils, by @kjfverhoeven.bsky.social and others. #landuse #hedgerowsoils
doi.org/10.1016/j.ag...

12.02.2026 14:38 👍 0 🔁 0 💬 0 📌 0
Source: Oldiefan, Pixabay (CC0)

Source: Oldiefan, Pixabay (CC0)

New publication: Female #chronotype relates to lay date but not #fitness in an island population of great tits, by @aureliastrauss.bsky.social, @babimt.bsky.social, @mevisser.bsky.social, and others. #greattits #laydate
doi.org/10.1007/s004...

12.02.2026 13:19 👍 1 🔁 2 💬 0 📌 0
Figure 1 Bogatinoska (2025): Digital elevation model including the river network (left) and soil map (right) of the Aa of Weerijs catchment.

Figure 1 Bogatinoska (2025): Digital elevation model including the river network (left) and soil map (right) of the Aa of Weerijs catchment.

New publication: Bridging technical insights and #stakeholder perspectives: The role of #models in environmental planning, by @stefandekker.bsky.social and others. #environmentalplanning
doi.org/10.1017/wat....

12.02.2026 11:56 👍 0 🔁 0 💬 0 📌 0
Figure 3 Delavaux (2026): Major traits hypothesized to impact the mutualist filter. A framework synthesizing mutualism traits hypothesized to impact the strength of the mutualist filter. Plant host traits include specificity, dependency, and multiple mutualists; mutualist traits include dispersal limitation, specificity, and dependency. Finally, species introductions may mediate the filter, with differing effects on the mainland relative to islands. An example within the mycorrhizal symbiosis contrasting arbuscular mycorrhizal (AM) and ectomycorrhizal (EM) mutualisms is given in the dark gray boxes. Although EM mutualisms are relatively stronger in three out of five traits predicted to increase the mutualist filter, research shows that AM plant species experience a stronger filter, likely due to the overriding effect of dispersal limitation.

Figure 3 Delavaux (2026): Major traits hypothesized to impact the mutualist filter. A framework synthesizing mutualism traits hypothesized to impact the strength of the mutualist filter. Plant host traits include specificity, dependency, and multiple mutualists; mutualist traits include dispersal limitation, specificity, and dependency. Finally, species introductions may mediate the filter, with differing effects on the mainland relative to islands. An example within the mycorrhizal symbiosis contrasting arbuscular mycorrhizal (AM) and ectomycorrhizal (EM) mutualisms is given in the dark gray boxes. Although EM mutualisms are relatively stronger in three out of five traits predicted to increase the mutualist filter, research shows that AM plant species experience a stronger filter, likely due to the overriding effect of dispersal limitation.

New publication: On the role of #mutualisms in #plant #biogeography: consequences for ecology, evolution, and invasion, by @camilledelavaux.bsky.social.
doi.org/10.1111/nph....

12.02.2026 11:07 👍 4 🔁 2 💬 0 📌 0
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We are looking for a PhD candidate to enhance soil biodiversity in road-side tree cultivation. You will work in a transdisciplinary consortium.

Find the vacancy on our website: nioo.knaw.nl/en/vacancies...

#vacancy #Wageningen

29.01.2026 13:53 👍 1 🔁 1 💬 0 📌 0
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Van de Waddenzee tot Taimyr: de reis en uitdagingen van rotganzen volgen Elk voorjaar maken rotganzen een indrukwekkende reis van gematigde streken naar de Russische toendra. Onderweg worden ze voortdurend geconfronteerd met uitdagingen en moeten ze hun lichamelijke condit...

Wat voor effect hebben de omstandigheden op de #Wadden op de #trek van #rotganzen? Hier houdt Jan Geisler zich tijdens zijn #PhD bij het NIOO mee bezig.

Lees de blog die hij schreef over zijn #onderzoek: nioo.knaw.nl/nl/blogs/van...

#Vogeltrek #Waddenzee #Trekvogels

27.01.2026 07:05 👍 3 🔁 2 💬 0 📌 0
Zhaoqi Bin at the end of her thesis defence together with her paranymphs

Zhaoqi Bin at the end of her thesis defence together with her paranymphs

Today Zhaoqi Bin defended her PhD thesis, titled “Application of trait-based plant-soil feedback for agroecosystem optimization”. The defence took place at Wageningen University. Congratulations Dr. Bin!

23.01.2026 16:23 👍 0 🔁 0 💬 1 📌 0
Figure 5 Mortier (2025): Fungi from Honduras. A. Schizophyllum commune; B. Hydnellum sp.; C. Beauveria caledonica; D. Aseroe rubra; E. Chlorociboria sp.; F. Xeromphalina enigmatica; G. Calostoma sp.; H. A species of Gomphaceae; I. Lentinus crinitus; J. Erioscyphella brasiliensis; K. Hymenochaete cinnamomea; L. Trechispora hondurensis. All photos were taken in Cusuco National Park, located in northwestern Honduras.

Figure 5 Mortier (2025): Fungi from Honduras. A. Schizophyllum commune; B. Hydnellum sp.; C. Beauveria caledonica; D. Aseroe rubra; E. Chlorociboria sp.; F. Xeromphalina enigmatica; G. Calostoma sp.; H. A species of Gomphaceae; I. Lentinus crinitus; J. Erioscyphella brasiliensis; K. Hymenochaete cinnamomea; L. Trechispora hondurensis. All photos were taken in Cusuco National Park, located in northwestern Honduras.

New publication: The first #checklist of #fungi known for #Honduras: revealing taxonomic geographical and functional trends.
doi.org/10.3897/myco...

13.01.2026 11:52 👍 2 🔁 1 💬 0 📌 0