Martin K. Obrist’s research while affiliated with Swiss Federal Institute for Forest, Snow and Landscape Research WSL and other places

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Publications (132)


Consumer biodiversity increases organic nutrient availability across aquatic and terrestrial ecosystems
  • Article

October 2024

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290 Reads

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1 Citation

Science

J Ryan Shipley

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[...]

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Human land-use intensification threatens arthropod (for example, insect and spider) biodiversity across aquatic and terrestrial ecosystems. Insects and spiders play critical roles in ecosystems by accumulating and synthesizing organic nutrients such as polyunsaturated fatty acids (PUFAs). However, links between biodiversity and nutrient content of insect and spider communities have yet to be quantified. We relate insect and spider richness to biomass and PUFA-mass from stream and terrestrial communities encompassing nine land uses. PUFA-mass and biomass relate positively to biodiversity across ecosystems. In terrestrial systems, human-dominated areas have lower biomass and PUFA-mass than more natural areas, even at equivalent levels of richness. Aquatic ecosystems have consistently higher PUFA-mass than terrestrial ecosystems. Our findings reinforce the importance of conserving biodiversity and highlight the distinctive benefits of aquatic biodiversity.


Estimated marginal means of linear temporal trends for carabid community traits in dominant local land‐use types. Squares represent estimated change in community weighted means (CWM) with 95% confidence intervals. Circles represent expected change in (non‐weighted) community means (CM, i.e. only variation due to species turnover) with 95% confidence intervals. Significantly (alpha = 0.05) positive trends (blue), significantly negative trends (red) and non‐significant trends (grey) are represented with colours. Upper panels show (standardised) temporal trait changes at the local pitfall trap level for each land‐use type. Lower panels show (standardised) temporal trait changes at the regional level. Changes refer to the linear expected change in the standardised response variable every 1SD of the variable year (~10 years for comparability). L. Activity period = length of activity period.
Estimated marginal means of linear temporal trends for spider community traits in dominant local land‐use type. Squares represent expected change in (CWM) with 95% confidence intervals. Circles represent expected change in (non‐weighted) community means (CM, i.e. only variation due to species turnover) with 95% confidence intervals. Significantly (alpha = 0.05) positive trends (blue), significantly negative trends (red) and non‐significant trends (grey) are represented with colours. Upper panels show (standardised) temporal trait changes at the local pitfall trap level in each land‐use type. Lower panels show (standardised) temporal trait changes at the regional level. Changes refer to the linear expected change in the response variable every 1SD of the variable year (~10 years for comparability). L. Activity period = length of activity period.
Effect of landscape‐level urbanisation and woody area loss on the four community‐weighted carabid trait means (CWM): body size, length of activity period, drought tolerance, and dispersal capacity. The t‐value of the interaction term (landscape change class × time) shows differences in trait CWM inter‐annual trends across more and less urbanised landscapes (or landscapes with a higher or lower decrease in woody area). A negative t‐value means a steeper decreasing trend or less pronounced increase of CWM trait values in landscapes highly urbanised or that lost woody area, respectively. The yellow bar represents the interaction t‐value of the model including all years with data, and the blue ones represent models missing a single year each time (i.e. leave‐one‐out jackknife procedure). The two dotted black lines determine the area of non‐significant differences in trends. Coloured squares represent the slope for each landscape category independently (higher urbanisation or woody area loss = top square, and lower urbanisation or woody area loss = bottom square). Grey for non‐significant trends, blue for significantly positive and red for significantly negative trends (alpha = 0.05).
Effect of landscape‐level urbanisation and woody area loss on the four community‐weighted spider trait means (CWM): body size, length of activity period, drought tolerance and dispersal capacity. The t‐value of the interaction term (landscape change class × time) shows differences in trait CWM inter‐annual trends across more and less urbanised landscapes (or landscapes with a higher or lower decrease in woody area). A negative t‐value a steeper decreasing trend or less pronounced increase of CWM trait values in more urbanised landscapes (or that lost more woody area) compared to those that suffered less urbanisation (or loss of woody area). The yellow bar represents the interaction t‐value of the model including all years, and the blue ones represent models missing a single year each time (i.e. leave‐one‐out jackknife procedure). The two dotted black lines determine the area of non‐significant differences in trends. Coloured squares represent the slope for each landscape category independently (higher urbanisation or woody area loss = top square, and lower urbanisation or woody area loss = bottom square). Grey for non‐significant trend, blue for significantly positive and red for significantly negative trends (alpha = 0.05).
Land‐use change in the past 40 years explains shifts in arthropod community traits
  • Article
  • Full-text available

March 2024

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347 Reads

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5 Citations

Understanding how anthropogenic activities induce changes in the functional traits of arthropod communities is critical to assessing their ecological consequences. However, we largely lack comprehensive assessments of the long‐term impact of global‐change drivers on the trait composition of arthropod communities across a large number of species and sites. This knowledge gap critically hampers our ability to predict human‐driven impacts on communities and ecosystems. Here, we use a dataset of 1.73 million individuals from 877 species to study how four functionally important traits of carabid beetles and spiders (i.e. body size, duration of activity period, tolerance to drought, and dispersal capacity) have changed at the community level across ~40 years in different types of land use and as a consequence of land use changes (that is, urbanisation and loss of woody vegetation) at the landscape scale in Switzerland. The results show that the mean body size in carabid communities declined in all types of land use, with particularly stronger declines in croplands compared to forests. Furthermore, the length of the activity period and the tolerance to drought of spider communities decreased in most land use types. The average body size of carabid communities in landscapes with increased urbanisation in the last ~40 years tended to decrease. However, the length of the activity period, the tolerance to drought, and the dispersal capacity did not change significantly. Furthermore, urbanisation promoted increases in the average dispersal capacities of spider communities. Additionally, urbanisation favoured spider communities with larger body sizes and longer activity periods. The loss of woody areas at the landscape level was associated with trait shifts to carabid communities with larger body sizes, shorter activity periods, higher drought tolerances and strongly decreased dispersal capacities. Decreases in activity periods and dispersal capacities were also found in spider communities. Our study demonstrates that human‐induced changes in land use alter key functional traits of carabid and spider communities in the long term. The detected trait shifts in arthropod communities likely have important consequences for their functional roles in ecosystems.

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Similar temporal patterns in insect richness, abundance and biomass across major habitat types

November 2023

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421 Reads

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2 Citations

Insect Conservation and Diversity

While many studies on insect diversity report declines, others show stable, fluctuating or increasing trends. For a thorough understanding of insect trends and their effects on ecosystem functioning, it is important to simultaneously assess insect richness, abundance and biomass, and to report trends for multiple taxa. We analysed insect richness, abundance and biomass data for all insects and for eight insect taxa (Buprestidae, Cerambycidae, Carabidae, other Coleoptera, Aculeata, other Hymenoptera, Heteroptera and Lepidoptera) from 42 sites across Switzerland from 2000 to 2007, representing three major habitat types in Switzerland (agricultural, unmanaged [open and forested] and managed forest habitats). As potential drivers of temporal patterns, we evaluated weather‐ and land‐use‐related factors. As predictors, we included temperature and precipitation as well as the vegetation index and the habitat type, respectively. We found a consistent pattern of stable or increasing trends for richness, abundance and biomass of insects in total and the eight taxa over 8 years. Both overall patterns and six out of eight taxa (except for Cerambycidae and Lepidotpera) showed the highest values in agricultural habitats. However, when accounting for elevation, there was no difference in open habitats regardless of whether they were used agriculturally. Habitat types were the most important predictors, followed by weather‐ and vegetation‐related factors. Modelled responses to mean temperature were unimodal, whereas the standard deviation of temperature showed positive and precipitation negative effects. Longer time series are needed to draw robust inferences and to investigate potential negative effects of future warming.


Global distribution of data included in this study
A Locations of sampling plots (orange dots) for all six taxonomic groups combined. All data are from the UrBioNet contributor network except for birds (eBird). B Ridgeline plots show the density of sampling locations per taxon as a function of latitude. See Supplementary Fig. 1 for taxon-specific maps.
Predicted changes in trait values per taxon along an urbanisation gradient
Partial dependence plots showing the urbanisation-induced shifts in community functional metrics for six taxonomic groups. The partial dependence plots summarise the marginal effect that urbanisation (x-axis = percentage of urbanised area in a 500 m radius around the sampling plot; or 1000 m for birds) has on the predicted values of each community-level trait (i.e. effect of urbanisation when climate, latitude and forest cover are kept constant). The y-axes reflect the range of predicted values for each response variable (community-weighted mean trait values and diversity metrics) and are not zeroed so care should be taken when interpreting the magnitude of change. The fitted colour lines and 95% confidence bands around predicted values are from Local Polynomial Regression (LOESS). The grey lines and 95% confidence bands around predicted values (light grey) are from linear regressions based on the same data to indicate direction of trend. Trait definitions are provided in Supplementary Table 3 (briefly, Feeding: high values = generalist diet except for bats where feeding represents different hunting strategy; Mobility: high values = higher mobility; Reproduction: amphibians, birds and reptile = clutch size / other taxa = reproduction strategy). Note that for bees, the inter-tegula distance was used for body size and mobility, and therefore the model presented is the same for both traits. Functional dispersion (FDis), functional richness (FRic) and functional evenness (FEve) are defined in the method section in “Functional composition of animal communities” (see also Supplementary Fig. 2). Transparent shade represents models with <10% variance explained. Stars show the contribution of urbanisation to the overall model (* 20-50%; ** > 50%). Additional information on each models’ overall predictive power and the contribution of the percentage of urban land cover can be found in Table 1. Image credits: Ghedo and T. Michael Keesey (https://creativecommons.org/licenses/by-sa/3.0/) for reptile. Michael Keesey (vectorization); Thorsten Assmann, Jörn Buse, Claudia Drees, Ariel-Leib-Leonid Friedman, Tal Levanony, Andrea Matern, Anika Timm, and David W. Wrase (photography) (https://creativecommons.org/licenses/by/3.0) for carabid beetle. All other silhouette images come from www.phylopic.org and are public domain images.
Relative importance of the extent and aggregation of urban land cover as predictors of community means (colours show the different trait categories; Supplementary Table 3) and variability (FDis = functional dispersion, FRic = functional richness, and FEve = functional evenness; dark blue) of traits as well as species richness for each taxonomic group
Variable importance was estimated using the residual sum of squares from random forests models. Average variable importance values weighted by the R² of the test set of each individual model were computed to estimate urban land cover variable importance for each metric of community-weighted means and variability of traits. Longer bars indicate traits or functional diversity measures that are better predicted by urban land cover within the surrounding landscape. Image credits: Idem Fig. 2.
Relative importance of variables in predicting trait responses per taxon
Importance of percent cover (%) and spatial aggregation (agg) of urban and forest land cover at different buffer distances (100 m and 500 m for most taxa; 1000 m for birds), latitude, climate PCA axes, and spatial covariates (dbMEM) as predictors of the trait syndrome (i.e. considering all community weighted means and functional diversity metrics) for each taxonomic group. Variable importance was estimated using the residual sum of squares from random forests models. Average values weighted by the R² of the test set of each individual model were computed to estimate variable importance for the overall trait syndromes. Image credits: Idem Fig. 2.
Simplified representation of the four urban trait syndromes
Two types of green habitat patches with different resources are represented in an otherwise mostly unsuitable urban matrix. Grey patches represent green habitats that are unusable for a specific taxon. Red dashed lines show typical movement pattern of taxa among patches. The landscapes of Fig. 5 and their individual elements were created by Bertrand Fournier using the basic set of tools available in the vector graphics open source software “Inkscape 1.2.2”. No previously-created elements were used. No images from a database were used. The landscapes of Fig. 5 and their individual elements were not published elsewhere. Image credits for taxa silhouettes: Idem Fig. 2.
Urbanisation generates multiple trait syndromes for terrestrial taxa worldwide

August 2023

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2,287 Reads

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48 Citations

Cities can host significant biological diversity. Yet, urbanisation leads to the loss of habitats, species, and functional groups. Understanding how multiple taxa respond to urbanisation globally is essential to promote and conserve biodiversity in cities. Using a dataset encompassing six terrestrial faunal taxa (amphibians, bats, bees, birds, carabid beetles and reptiles) across 379 cities on 6 continents, we show that urbanisation produces taxon-specific changes in trait composition, with traits related to reproductive strategy showing the strongest response. Our findings suggest that urbanisation results in four trait syndromes (mobile generalists, site specialists, central place foragers, and mobile specialists), with resources associated with reproduction and diet likely driving patterns in traits associated with mobility and body size. Functional diversity measures showed varied responses, leading to shifts in trait space likely driven by critical resource distribution and abundance, and taxon-specific trait syndromes. Maximising opportunities to support taxa with different urban trait syndromes should be pivotal in conservation and management programmes within and among cities. This will reduce the likelihood of biotic homogenisation and helps ensure that urban environments have the capacity to respond to future challenges. These actions are critical to reframe the role of cities in global biodiversity loss.


Towards a General Approach for Bat Echolocation Detection and Classification

December 2022

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292 Reads

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9 Citations

Acoustic monitoring is an effective and scalable way to assess the health of important bioindicators like bats in the wild. However, the large amounts of resulting noisy data requires accurate tools for automatically determining the presence of different species of interest. Machine learning-based solutions offer the potential to reliably perform this task, but can require expertise in order to train and deploy. We propose BatDetect2, a novel deep learning-based pipeline for jointly detecting and classifying bat species from acoustic data. Distinct from existing deep learning-based acoustic methods, BatDetect2’s outputs are interpretable as they directly indicate at what time and frequency a predicted echolocation call occurs. BatDetect2 also makes use of surrounding temporal information in order to improve its predictions, while still remaining computationally efficient at deployment time. We present experiments on five challenging datasets, from four distinct geographical regions (UK, Mexico, Australia, and Brazil). BatDetect2 results in a mean average precision of 0.88 for a dataset containing 17 bat species from the UK. This is significantly better than the 0.71 obtained by a traditional call parameter extraction baseline method. We show that the same pipeline, without any modifications, can be applied to acoustic data from different regions with different species compositions. The data annotation, model training, and evaluation tools proposed will enable practitioners to easily develop and deploy their own models. BatDetect2 lowers the barrier to entry preventing researchers from availing of effective deep learning bat acoustic classifiers. Open source software is provided at: https://github.com/macaodha/batdetect2


Increased arthropod biomass, abundance and species richness in an agricultural landscape after 32 years

December 2022

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827 Reads

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11 Citations

Journal of Insect Conservation

Recent studies reporting widespread declines in arthropod biomass, abundance and species diversity raised wide concerns in research and conservation. However, repeated arthropod surveys over long periods are rare, even though they are key for assessing the causes of the decline and for developing measures to halt the losses. We repeatedly sampled arthropod fauna in a representative Swiss agricultural landscape over 32 years (1987, 1997, 2019). Sampling included eight study sites in four different semi-natural and agricultural habitat types and different trap types (pitfall, window, yellow bucket) over an annual period of 10 weeks to capture flying and ground dwelling arthropod taxa. In total, we analyzed 58,448 individuals from 1343 different species. Mean arthropod biomass, abundance and species richness per trap was significantly higher in 2019 than in the prior years. Also, species diversity of the study area was highest in 2019. Three main factors likely have contributed to the observed positive or at least stable development. First, the implementation of agri-environmental schemes has improved habitat quality since 1993, 6 years after the first sampling. Second, landscape composition remained stable, and pesticide and fertilizer was constant over the study period. Third, climate warming might have favored the immigration and increase of warm adapted species. Our results support the idea that changes in arthropod communities over time is highly context-dependent and complex. Implications for insect conservation We conclude that the integration and long-term management of ecological compensation patches into a heterogenous agricultural landscape supports insect conservation and can contribute to stable or even increased arthropod abundance, biomass and diversity. Future studies are needed to clarify interdepending effects between agricultural management and climate change on insect communities.


Fig. 1. Schematic representation of four hypothetical landscapes on the gradients of disturbance severity and extent. Each landscape consists of four forest stands. Dark green and brown trees represent undisturbed and disturbed parts of a stand, respectively. (A) Landscape where all stands are disturbed, but the disturbance severity within the stands is low; (B) landscape where all stands are severely disturbed; (C) landscape where most stands have not been affected by disturbance and the disturbance severity within a disturbed stand is low; (D) landscape where most stands have not been affected by disturbance, but the disturbance severity within a disturbed stand is high.
Fig. 2. The locations of study sites (N = 70) included in the meta-analysis. Classification of biomes is based on Olson et al. (2001).
Fig. 3. Differences in α-diversity between naturally disturbed and undisturbed forests categorised by taxonomic group. (A) Black dots represent weighted mean effect sizes transformed to percentage differences in species richness, coloured circles correspond to each data point. Asterisks against group names indicate significant effects (p < 0.05) in the mixed-effects meta-analysis. (B) Proportions of disturbed forest that correspond to the maximal mixture diversity of each taxonomic group. Dots represent the means of data points and whiskers show respective standard deviations. Whiskers are missing when only one incidence matrix for a taxonomic group was available.
Fig. 5. Response of species richness to the proportion of disturbed area in the forest landscape. The curves and confidence intervals (shading) are generated by fitting the LOESS function. Components of species richness: species unique to disturbed forests; species unique to undisturbed forests; a mixture of both groups of unique species and species shared between two habitat types, i.e. mixture diversity.
Results of the beta-regression with the proportion of disturbed forest corresponding to highest mixture diversity as a response variable. Wald tests on terms were applied to test for significance.
The effect of natural disturbances on forest biodiversity: an ecological synthesis

September 2022

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1,900 Reads

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80 Citations

Biological reviews of the Cambridge Philosophical Society

Disturbances alter biodiversity via their specific characteristics, including severity and extent in the landscape, which act at different temporal and spatial scales. Biodiversity response to disturbance also depends on the community characteristics and habitat requirements of species. Untangling the mechanistic interplay of these factors has guided disturbance ecology for decades, generating mixed scientific evidence of biodiversity responses to disturbance. Understanding the impact of natural disturbances on biodiversity is increasingly important due to human-induced changes in natural disturbance regimes. In many areas, major natural forest disturbances, such as wildfires, windstorms, and insect outbreaks, are becoming more frequent, intense, severe, and widespread due to climate change and land-use change. Conversely, the suppression of natural disturbances threatens disturbance-dependent biota. Using a meta-analytic approach, we analysed a global data set (with most sampling concentrated in temperate and boreal secondary forests) of species assemblages of 26 taxonomic groups, including plants, animals, and fungi collected from forests affected by wildfires, windstorms, and insect outbreaks. The overall effect of natural disturbances on α-diversity did not differ significantly from zero, but some taxonomic groups responded positively to disturbance, while others tended to respond negatively. 2 Mari-Liis Viljur and others Disturbance was beneficial for taxonomic groups preferring conditions associated with open canopies (e.g. hymenopterans and hoverflies), whereas ground-dwelling groups and/or groups typically associated with shady conditions (e.g. epigeic lichens and mycorrhizal fungi) were more likely to be negatively impacted by disturbance. Across all taxonomic groups, the highest α-diversity in disturbed forest patches occurred under moderate disturbance severity, i.e. with approximately 55% of trees killed by disturbance. We further extended our meta-analysis by applying a unified diversity concept based on Hill numbers to estimate α-diversity changes in different taxonomic groups across a gradient of disturbance severity measured at the stand scale and incorporating other disturbance features. We found that disturbance severity negatively affected diversity for Hill number q = 0 but not for q = 1 and q = 2, indicating that diversity-disturbance relationships are shaped by species relative abundances. Our synthesis of α-diversity was extended by a synthesis of disturbance-induced change in species assemblages, and revealed that disturbance changes the β-diversity of multiple taxonomic groups, including some groups that were not affected at the α-diversity level (birds and woody plants). Finally, we used mixed rarefaction/extrapolation to estimate biodiversity change as a function of the proportion of forests that were disturbed, i.e. the disturbance extent measured at the landscape scale. The comparison of intact and naturally disturbed forests revealed that both types of forests provide habitat for unique species assemblages, whereas species diversity in the mixture of disturbed and undisturbed forests peaked at intermediate values of disturbance extent in the simulated landscape. Hence, the relationship between α-diversity and disturbance severity in disturbed forest stands was strikingly similar to the relationship between species richness and disturbance extent in a landscape consisting of both disturbed and undisturbed forest habitats. This result suggests that both moderate disturbance severity and moderate disturbance extent support the highest levels of biodiversity in contemporary forest landscapes.


Fig. 1. The distribution of the 18 selected study locations (maternity roosts of M. myotis) overlaid on the known distribution of M. myotis shown as red (data from 2001 to 2020) and orange (data from 1903 to 2000) 5x5 km squares (InfoFauna, 2020).
Fig. 2. Sampling design with four triplets of sampling sites (predicted as suitable, intermediate and unsuitable, respectively) in the forests around the maternity roost of M. myotis in Burgdorf. The circle defines the sampling area of 5 km around the roost. The design was repeated around 18 different maternity roosts.
Fig. 4. A selection of field variables displaying forest structures on the x-axis and activity of M. myotis on the y-axis.Left side: Activity vs. continuous variables of coverages and flight space with a dashed smooth curve. Right side: Box plot of activity vs. categorical variables (with log transformed activity scales). Background colours match those in Fig. 3.
Fig. 5. GLMM of remote sensing data. All remote sensing variables are marked with RS. Incidence rate ratio is the ratio between the activity of M. myotis per night attributable to the expressed variable and the total number of M. myotis activity. The higher the incidence rate ratio > 1, the more the activity of M. myotis is positively affected by this variable (black). The lower the incidence rate ratio < 1, the more the activity of M. myotis is negatively affected (grey).
selection of the most important forest variables recorded at sampling sites and retained in the final model. For more details see Appendix S3.
LiDAR metrics predict suitable forest foraging areas of endangered Mouse-eared bats (Myotis myotis)

July 2022

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322 Reads

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11 Citations

Forest Ecology and Management

Habitat shift caused by human impact on vegetation structure poses a great threat to species which are specialized on unique habitats. Single layered beech forests, the main foraging habitat of Greater Mouse-eared Bats (Myotis myotis), are threatened by recent changes in forest structure. After this species suffered considerable population losses until the 1970s, their roosts in buildings are strictly protected. However, some populations are still declining. Thus, the spatial identification of suitable foraging habitat would be essential to ensure conservation policy. The aim of this study was (a) to verify the relevance of forest structural variables for the activity of M. myotis and (b) to evaluate the potential of LiDAR (Light Detection and Ranging) in predicting suitable foraging habitat of the species. We systematically sampled bat activity in forests close to 18 maternity roosts in Switzerland and applied a generalized linear mixed model (GLMM) to fit the activity data to forest structure variables recorded in the field and derived from LiDAR. We found that suitable forest foraging habitat is defined by single layered forest, dense canopy, no shrub layer and a free flight space. Most importantly, this key foraging habitat can be well predicted by airborne LiDAR data. This allows for the first time to create nationwide prediction maps of potential foraging habitats of this species to inform conservation management. This method has a special significance for endangered species with large spatial use, whose key resources are hard to identify and widely distributed across the landscape.


Contrasting impacts of street light shapes and LED color temperatures on nocturnal insects and bats

July 2022

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99 Reads

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11 Citations

Basic and Applied Ecology

Street lights are important light sources that contribute to artificial light at night (ALAN). To date, ecological impacts of individual LED properties (color temperature, dimmability) have been studied, while interactions between light properties or aspects of luminaire design have not been addressed. However, the design of luminaires can influence ALAN impacts as the shape determines the spatial distribution of light and its visibility in the environment. This may cause amplifying or mitigating effects. We assessed the relative individual and interacting effects of two LED luminaire designs and three LED color temperatures (1750 K, 3000 K, 4000 K) on nocturnal insect abundance, bat foraging and feeding activity. We considered a standard LED luminaire shape with focused light emission and a luminaire shape with a diffusor to scatter the light spatially, leading to increased visibility of the light in the environment. During 104 nights, we trapped 51263 nocturnal insects of which 97% were caught at lights and 3% at dark sites. For bats, up to 44.8% fewer acoustic signals were recorded at dark sites. We caught 31% insects at LEDs with1750 K, 34% and 35% at 3000 K and 4000 K, respectively. Thus, color temperatures of 1750 K proved less detrimental than 3000/4000 K. Effects of luminaire shape led to an increase (16%) of trapped insects for luminaires with diffusors compared to the standard shape. In addition, luminaires with diffusors amplified the effects of LED color (+12% insects at 1750 K/3000 K; +25.6% at 4000 K). In contrast, bat foraging activity was independent of the light treatments while bat feeding activity was increased by 21.5% at standard luminaire shapes. Likely, intense straylight at diffused lights negatively affects the target-focused echolocation by deterring the bats. We concluded that ecological impacts of luminaire shape are an important, yet underestimated variable in light-pollution impact research.


Recent trends in stream macroinvertebrates: warm-adapted and pesticide-tolerant taxa increase in richness

March 2022

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439 Reads

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14 Citations

Recently, a plethora of studies reporting insect declines has been published. Even though the common theme is decreasing insect richness, positive trends have also been documented. Here, we analysed nationwide, systematic monitoring data on aquatic insect richness collected at 438 sites in Switzerland from 2010 to 2019. In addition to taxonomic richness, we grouped taxa in accordance with their ecological preferences and functional traits to gain a better understanding of trends and possible underlying mechanisms. We found that in general, richness of aquatic insects remained stable or increased with time. Warm-adapted taxa, common feeding guilds and pesticide-tolerant taxa showed increasing patterns while cold-adapted, rarer feeding guilds and pesticide-sensitive taxa displayed stable trends. Both climate and land-use-related factors were the most important explanatory variables for the patterns of aquatic insect richness. Although our data cover the last decade only, our results suggest that recent developments in insect richness are context-dependent and affect functional groups differently. However, longer investigations and a good understanding of the baseline are important to reveal if the increase in temperature- and pesticide-tolerant species will lead to a decrease in specialized species and a homogenization of biotic communities in the long term.


Citations (57)


... Apart from this, all three species are nevertheless generalists with a broad ecological amplitude. This is also true for species in Group B, which are also euryoecious with a focus on mesic grassland ecosystems (Nyffeler and Breene 1990;Martin 2020). Of particular interest here is the separation of Erigone dentipalpis and Erigone atra. ...

Reference:

From lawns to meadows: spiders (Arachnida: Araneae) as indicators to measure urban grassland restoration success
Land‐use change in the past 40 years explains shifts in arthropod community traits

... Long-term research and recent reviews have described dramatic (60%-85%) declines in arthropod biomass (Montgomery et al., 2020Wagner, 2020 in Europe (Hallmann et al., 2017), North America (Harris et al., 2019Wepprich et al., 2019, the tropics (Janzen & Hallwachs, 2019), and the Arctic (Abrego et al., 2021Høye et al., 2013Loboda et al., 2018. However, recent findings of increasing moth biomass in boreal forests of Finland during 1993-2019 (Yazdanian et al., 2023), and studies with similar results (e.g., Gebert et al., 2023Hunter et al., 2014, indicate such declines are by no means worldwide. In addition to population declines, most species extinctions are estimated to be of undocumented insects (Dunn, 2005) and increasing at such a rate that the Earth may be entering its sixth mass extinction event (Ceballos et al., 2015). ...

Similar temporal patterns in insect richness, abundance and biomass across major habitat types

Insect Conservation and Diversity

... Insectivorous bird species richness and vocalization-based functional diversity decreased with increasing urbanization within the boundaries of the city of Montreal. These findings are consistent with the longstanding theory that urbanization causes a reduction in the complexity of ecological communities (McKinney, 2006) as well as functional homogenization with more generalist species, which display greater resilience to human disturbances (Hahs et al., 2023). Research focusing on birds confirmed this general trend, both locally (Marcacci et al., 2021;Palacio et al., 2018;Santos et al., 2024) and globally (Sol et al., 2020). ...

Urbanisation generates multiple trait syndromes for terrestrial taxa worldwide

... and BatDetect2 and BatNet for bats (Aodha et al., 2022;Krivek et al., 2023) in sound recordings. Additionally, customised models can be trained on open datasets, for example, FathomNet for marine organisms (Katija et al., 2022), Pl@ntNet for plants and iNaturalist for a range of different species. ...

Towards a General Approach for Bat Echolocation Detection and Classification
  • Citing Preprint
  • December 2022

... The relationship between wing length and body weight has been widely used for estimating biomass in terrestrial, benthic, and planktonic invertebrates. This relationship finds applications in ecological studies, including characterizing ecological communities (Schoener, 1980), comparing populations within and between habitats and ecosystems (Benke et al., 1999), exploring energetically-based interspecific relationships (Benke, 1993), and tracking habitat change (Fürst et al., 2022) and long-term population changes (Macgregor et al., 2019, Hallmann et al., 2020, Kinsella et al., 2020. Despite its significance, comparative studies of body size across species and geographic regions pose challenges. ...

Increased arthropod biomass, abundance and species richness in an agricultural landscape after 32 years

Journal of Insect Conservation

... Exposure to artificial light at night (ALAN) has been shown to alter the behavior of many organisms, which may disrupt predator-prey interactions. Positive phototaxis may locally increase prey abundance and this usually attracts predators (McMunn et al., 2019;Willmott et al., 2019;Nelson et al., 2020;Bolliger et al., 2022). Increased availability of prey benefits nocturnal predators as has been shown for some insectivorous bats (Frank et al., 2018;Bolliger et al., 2022). ...

Contrasting impacts of street light shapes and LED color temperatures on nocturnal insects and bats
  • Citing Article
  • July 2022

Basic and Applied Ecology

... Even though we often search for prevailing theoretical expectations and empirical patterns, for example, a monotonic positive SAR, or unimodal PDR and DDR, these expectations fail to capture the full complexity of these relationships. As a result, it is not surprising, and perhaps even expected, that we would find considerable variation in biodiversity responses to multiple drivers within and among empirical studies (Cusens et al., 2012;Fahrig, 2017;He et al., 2024;Mackey & Currie, 2001;Mittelbach et al., 2001;Svensson et al., 2012;Viljur et al., 2022;Whittaker, 2010). Although our results indicate that SAR, DDR, and PDR patterns can be highly variable, it is also not surprising that certain types of patterns are more often observed in natural communities. ...

The effect of natural disturbances on forest biodiversity: an ecological synthesis

Biological reviews of the Cambridge Philosophical Society

... Understory vegetation conditions that cause resistance to grizzly bear movement were considered alongside the risks from road disturbance, assessed by calculating road visibility across the landscape (Parsons et al. 2021). Habitat assessment for endangered mouse-eared bats (Myotis myotis) has also been enhanced by explicit consideration of its ecology and subsequent derivation of custom ALS predictors (Rauchenstein et al. 2022). Mouse-eared bats are understood to require closed canopy forests with sufficient space for flight maneuvers and a minimal understory layer to enable the bats to feed on flightless ground beetles (Rudolph et al. 2009). ...

LiDAR metrics predict suitable forest foraging areas of endangered Mouse-eared bats (Myotis myotis)

Forest Ecology and Management

... Especially, coldadapted species are prone to be negatively affected, putting many alpine species at risk (Engler et al. 2011;Dullinger et al. 2012;Theodoridis et al. 2018). However, these changes may also be advantageous for warm-tolerant species, with opportunities to expand their ranges to higher elevations (Engler et al. 2009;Vitasse et al. 2021;Gebert et al. 2022). For instance, Alpine plant diversity has seen an increase due to the upward movement of several species (Roth, Plattner, and Amrhein 2014), the average altitudinal distribution of breeding birds in Switzerland rose by 24 m between 1990 and 2010 (Knaus et al. 2018), and many aquatic insect species are also extending their range to higher elevation (Gebert et al. 2022). ...

Recent trends in stream macroinvertebrates: warm-adapted and pesticide-tolerant taxa increase in richness

... Fekete et al., 2019;Frosch et al., 2016;Shevchenko & Kolodochka, 2014). Furthermore, it is unclear how the conservation value of cemeteries compares with that of other types of urban green spaces, particularly parks, because urban biodiversity studies have tended to combine these two types of green spaces, thereby overlooking potentially meaningful differences (Pinho et al., 2021). Few studies have directly addressed this question, and the few that have show inconsistent patterns. ...

Research agenda on biodiversity and ecosystem functions and services in European cities
  • Citing Article
  • February 2021

Basic and Applied Ecology