Abstract:1. Severe losses of insects have taken place over major parts of Europe. This negative trend is assumed to be largely the result of agricultural intensification.2. To analyse potential factors causing this loss of species, we assessed butterfly communities at 21 grassland patches. Seventeen of these were distributed across an agricultural landscape dominated by crop fields; four were embedded in two adjoining managed semi-natural grassland areas. We assessed environmental parameters such as patch size and habi… Show more
“…Nocturnal lepidopterans are very rich in species and comparatively well understood in terms of taxonomy and ecology (Haslberger & Segerer, 2016; Hering, 1951; Kristensen, 1999; Scoble, 1995). Many representatives of this taxon react highly sensitive onto environmental changes such as land use intensification and the deterioration of habitat quality (Bayerisches Landesamt für Umweltschutz, LFU, 2003; Ekroos, Heliölä, & Kuussaari, 2010; Habel, Ulrich, Biburger, Seibold, & Schmitt, 2019; Sánchez‐Bayo & Wyckhuys, 2019). Thus, this second approach, automated light trapping and active sampling at a light tower, provided in total 3,738 individuals and 371 lepidopteran species, including 20 Red List species.…”
The number of insect species and insect abundances decreased severely during the past decades over major parts of Central Europe. Previous studies documented declines of species richness, abundances, shifts in species composition, and decreasing biomass of flying insects. In this study, we present a standardized approach to quantitatively and qualitatively assess insect diversity, biomass, and the abundance of taxa, in parallel. We applied two methods: Malaise traps, and automated and active light trapping. Sampling was conducted from April to October 2018 in southern Germany, at four sites representing conventional and organic farming. Bulk samples obtained from Malaise traps were further analyzed using DNA metabarcoding. Larger moths (Macroheterocera) collected with light trapping were further classified according to their degree of endangerment. Our methods provide valuable quantitative and qualitative data. Our results indicate more biomass and higher species richness, as well as twice the number of Red List lepidopterans in organic farmland than in conventional farmland. This combination of sampling methods with subsequent DNA metabarcoding and assignments of individuals according depending on ecological characteristics and the degree of endangerment allows to evaluate the status of landscapes and represents a suitable setup for large-scale long-term insect monitoring across Central Europe, and elsewhere.
“…Nocturnal lepidopterans are very rich in species and comparatively well understood in terms of taxonomy and ecology (Haslberger & Segerer, 2016; Hering, 1951; Kristensen, 1999; Scoble, 1995). Many representatives of this taxon react highly sensitive onto environmental changes such as land use intensification and the deterioration of habitat quality (Bayerisches Landesamt für Umweltschutz, LFU, 2003; Ekroos, Heliölä, & Kuussaari, 2010; Habel, Ulrich, Biburger, Seibold, & Schmitt, 2019; Sánchez‐Bayo & Wyckhuys, 2019). Thus, this second approach, automated light trapping and active sampling at a light tower, provided in total 3,738 individuals and 371 lepidopteran species, including 20 Red List species.…”
The number of insect species and insect abundances decreased severely during the past decades over major parts of Central Europe. Previous studies documented declines of species richness, abundances, shifts in species composition, and decreasing biomass of flying insects. In this study, we present a standardized approach to quantitatively and qualitatively assess insect diversity, biomass, and the abundance of taxa, in parallel. We applied two methods: Malaise traps, and automated and active light trapping. Sampling was conducted from April to October 2018 in southern Germany, at four sites representing conventional and organic farming. Bulk samples obtained from Malaise traps were further analyzed using DNA metabarcoding. Larger moths (Macroheterocera) collected with light trapping were further classified according to their degree of endangerment. Our methods provide valuable quantitative and qualitative data. Our results indicate more biomass and higher species richness, as well as twice the number of Red List lepidopterans in organic farmland than in conventional farmland. This combination of sampling methods with subsequent DNA metabarcoding and assignments of individuals according depending on ecological characteristics and the degree of endangerment allows to evaluate the status of landscapes and represents a suitable setup for large-scale long-term insect monitoring across Central Europe, and elsewhere.
“…Nilsson et al, 2008;Augenstein et al, 2012;Habel et al, 2016). Another frequently used method to examine potential drivers of insect declines is the space-for-time approach, in which the insect diversity in heavily impacted habitats is compared with diversity in less impacted or assumingly undisturbed (control) habitats at the same time (Habel et al, 2019). Still other studies are based on data of long-term monitoring projects (Conrad et al, 2006;Hallmann et al, 2017;Homburg et al, 2019).…”
Section: Discussionmentioning
confidence: 99%
“…Indeed, atmospheric nitrogen influxes from agriculture, industry and traffic negatively impact habitat quality, especially in nitrogen-limited ecosystems such as semi-natural grasslands (Wallis de Vries & Van Swaay, 2006). Furthermore, pesticides are known to negatively impact insect diversity, either directly due to drifting insecticides (Geiger et al, 2010), or indirectly by the elimination of potentially important larval food plants and/or nectar sources (for pollinating insects) with herbicides (González-Varo et al, 2013;Habel et al, 2019). In our study, 12 sites were distributed across agricultural landscapes dominated by crop fields (Fig.…”
Section: Discussionmentioning
confidence: 99%
“…Nonetheless, several other studies provided evidence that intensification of cropland is the major driver of the decline of insect abundance and species richness in agricultural landscapes (Ollerton et al, 2014;Thomas, 2016;Ernst et al, 2017). For example, negative impacts of intensive conventional agriculture on butterfly species richness and abundance were recorded in semi-natural grassland in Germany (Habel et al, 2019). Specialised butterfly species were mainly found in semi-natural grassland patches, and were largely absent from other grassland patches embedded in an intensively managed agricultural matrix.…”
Section: Discussionmentioning
confidence: 99%
“…Intensive agriculture entails the planting of large, uniform monocultures, the removal of trees and hedgerows in order to facilitate mechanisation and the recurrent use of pesticides for controlling crop pests (insecticides), competing weeds (herbicides) and fungal infections (fungicides; Dudley & Alexander, 2017). Intensified land use is shifting multiple insect communities towards species-poor assemblages dominated by a few generalist species, while specialist species are going extinct (White & Kerr, 2007;Habel et al, 2019;Sanchez-Bayo & Wyckhuys, 2019).…”
World‐wide decreases of insect abundance and diversity are of major concern because of their importance for ecosystem functioning and the stability of ecosystems. Various studies reported dramatic declines of butterflies, wild bees and beetles in agricultural areas. Yet, evidence for decreasing abundance in cryptic insect species is scarce.
Using a transect‐count technique, we monitored the relative population size of the endangered flightless grassland longhorn beetle Iberodorcardion fuliginator in 13 dry, semi‐natural grassland sites in the border region of Switzerland, France, and Germany at yearly intervals over 20 years (1999–2018). To disentangle potential causes for changes in I. fuliginator abundance over time, we recorded quantitatively the plant communities in all sites in 2004 and 2017 and changes in other habitat characteristics.
We found that the overall abundance of I. fuliginator individuals decreased by 90% over 20 years: at one site the population went extinct, at five sites the populations were critically decreasing, at four sites the populations were decreasing and at only three sites population size remained stable.
Linear models revealed that the factor ‘change in plant species composition’ is the main driver for the decrease in beetle abundance. Alternative models indicated that – in addition to vegetation changes – area of suitable habitat and low heat load affected the probability of decreasing population size.
Our study shows that gradual habitat deterioration measured as reduction in grass cover and change in plant species composition negatively affect the abundance of the highly specialised beetle I. fuliginator.
Maintaining the biodiversity of agricultural ecosystems has become a global imperative. Across Europe, species that occupy agricultural grasslands, such as black‐tailed godwits (Limosa limosa limosa), have undergone steep population declines. In this context, there is a significant need to both determine the root causes of these declines and identify actions that will promote biodiversity while supporting the livelihoods of farmers.
Food availability, and specifically earthworm abundance (Lumbricidae), during the pre‐breeding period has often been suggested as a potential driver of godwit population declines. Previous studies have recommended increasing the application of nitrogen to agricultural grasslands to enhance earthworm populations and aid agricultural production. Here we test whether food availability during the pre‐breeding period affects when and where godwits breed.
Using large‐scale surveys of food availability, a long‐term mark‐recapture study, focal observations of foraging female godwits, and tracking devices that monitored godwit movements, we found little evidence of a relationship between earthworm abundance and the timing of godwit reproductive efforts or the density of breeding godwits. Furthermore, we found that the soils of intensively managed agricultural grasslands may frequently be too dry for godwits to forage for those earthworms that are present.
The increased application of nitrogen to agricultural grasslands will therefore likely have no positive effect on godwit populations. Instead, management efforts should focus on increasing the botanical diversity of agricultural grasslands, facilitating conditions that prevent hardening soils, and reducing the populations of generalist predators.
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