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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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.
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.
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.
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.
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
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.
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.
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.
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.
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.
... 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. ...
... 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). ...
... 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). ...
... 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. ...
... 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. ...
... 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). ...
... 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. ...
... 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). ...
... 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). ...
... 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. ...