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Mountainous regions host globally unique biodiversity, but face growing threats from climate and land-use change. The Alps stand out as a key mountain range in Europe, where the ski industry is extensive and impacts ecosystems and their associated biodiversity. However, climate change is projected to reduce natural snow precipitation, thus understanding snow dynamics and the ski industry’s role is crucial for developing effective conservation strategies. Ski-piste creation generally has detrimental consequences for mountain biodiversity, yet pistes often retain substantial snow throughout spring that, when melting, may create favourable foraging conditions for mountain birds. This study investigates whether ski-pistes provide suitable foraging habitat and explores their broader importance for mountain avifauna. Field surveys in spring 2023 in the western Italian Alps recorded 17 bird species using the melting snow on ski-pistes as a foraging habitat. Snow presence was a significant factor influencing bird presence. Birds systematically selected areas with intermediate snow cover interspersed with muddy patches, a microhabitat that likely has a high availability of invertebrate prey emerging from the soil. Given that snow is retained on ski-pistes for longer than on the surrounding habitat, the pistes may represent a useful source of food for mountain birds in spring. However, this needs to be considered in relation to the negative impacts of skiing on alpine biodiversity, which may include a likely increased reliance on artificial snow in response to the projected decline in natural snow precipitation under climate change. Understanding these effects is essential to ensure that future conservation strategies support mountain bird communities without exacerbating the environmental costs associated with artificial snow production.
Invasive plants’ ability to extend their range depends upon their local environments and both positive and negative interactions with native species. Interactions between invasive and native plants may be indirectly linked to the soil fungal community, which may enhance or suppress invasion through mutualism or parasitism. Many invasive plants preferentially select fungal communities or change soil chemistry to gain a competitive advantage, and such changes can remain even after the invader is removed, known as legacy effects. Yellow toadflax (Linaria vulgaris Mill.) is an invasive forb that is aggressive in the western United States but is nonaggressive in the midwestern United States. We evaluated the relationship between soil abiotic properties, nitrogen (N) enrichment, arbuscular mycorrhizal fungal (AMF) community composition, and L. vulgaris invasion in aggressive (CO) and nonaggressive (IL) populations. We collected soil from uninvaded and invaded sites in Gothic, CO, and near Chicago, IL, and sequenced AMF community composition in each site. Using the same soil, we grew L. vulgaris and native species in pots for 120 d, with half of the pots receiving N fertilization, and harvested biomass. We also injected a 15N-labeled tracer in pots and analyzed plant tissue for 15N enrichment and net uptake rates (NUR). In CO soil, L. vulgaris rhizomes sprouted more in invaded soil, whereas in IL soil, L. vulgaris only sprouted in uninvaded soil. N fertilization had no impact on biomass, and NUR did not differ significantly between any treatments. AMF communities differed between the two sites but were not significantly influenced by invasion history. Our results suggest that L. vulgaris leaves legacy effects but that these effects are different between aggressive and nonaggressive populations. Legacy effects may facilitate reinvasion in CO, but we did not find conclusive evidence of legacy effects in IL, and differences between the sites could be shaped by endemic AMF communities.
This is a reprinting of Bohr’s response to the EPR paper, wherein Bohr relies on his principle of complementarity to demonstrate an ambiguity in the criterion of reality as described by EPR and to argue that quantum mechanics is in fact a complete description of reality given the bounds of complementarity.
This is a reprinting of Margenau’s response to EPR (and to some extent, his evaluation of previous responses to EPR by Bohr, Kemble and Ruark). Margenau’s contribution to the EPR debate is certainly one of the most original, no doubt at least in part due to the meaty correspondence he had with Einstein while producing it. Margenau’s main strategy in this paper is to argue against the standard collapse postulate of quantum mechanics, suggesting that the EPR argument only applies to quantum mechanics with this postulate added. He also argues against the statistical interpretation of the collapse postulate suggested by Kemble and others.
This is a reprinting from Jammer (1974) of Podolsky’s unpublished response to Kemble’s criticisms of the EPR paper. Podolsky rightly criticises Kemble for missing the point of EPR’s argument and adds a few comments agreeing with Kemble that a statistical interpretation of quantum mechanics is best – yet Podolsky maintains such an interpretation is incomplete.
This is a reprinting of Bohr’s note to Nature advertising his forthcoming response to the EPR paper. It is very brief but contains in essence the argumentative tack Bohr would in fact employ in his full response to EPR.
This is a reprinting of Edwin Kemble’s 1935 reply to the EPR paper. Kemble misses EPR’s point by taking their completeness criterion to be merely an epistemic concept; Kemble himself admits as much in a letter to Einstein later that year. His original response to EPR is nevertheless of interest, as Kemble there provides an argument for a statistical interpretation of the wavefunction – a view he attributes to Slater already in a 1929 paper, but for which Kemble provides greater clarity and motivation.
This is a reprinting of Furry’s response to Schrödinger’s cat paper and entanglement papers, as well as Furry’s response to other responses to the EPR paper, especially Bohr’s.
In this chapter, we dive deeply into Bohr’s views on (in)completeness and (non)locality. Perhaps the most outspoken and famous respondent to EPR, Bohr is generally thought to be obscure in his reply. We analyse it afresh (at least to our satisfaction), in particular in regard to its argumentative structure, the role of Bohr's examples and that of his 'non-mechanical disturbance'. We also assess its limitations as a reply to Einstein's wider concerns.
Paleoecological studies can provide some insight into factors influencing a species’ present-day distribution, and its present-day distribution can, in turn, provide some insight into its future distribution. Being able to predict future distributions is very important because climate, an important influence on species distribution, is now changing at a rapid rate. Within a population, individuals may have a random, uniform, or clumped dispersion, though a clumped dispersion is most common because essential resources such as food, light, and undisturbed habitat are often spatially clumped. Distribution patterns change over the short term, as a result of dispersal, and over the long term from factors that influence range expansion and contraction. Abiotic factors, such as climate, soils, light availability and disturbance, and biotic factors, such as behavior, life histories and interactions with other species, can influence the distribution of species. Changes in these factors can lead to changes in distribution, including range expansion, range contraction and extinction. By quantitatively describing a species’ ecological niche, ecologists can understand a species’ present distribution, and may be able to make predictions about its future distribution.
A non-equilibrium perspective sheds light on why conventional conservation may fail to achieve its objectives. The human history of societies and the evolutionary history of species have shaped adaptations to disturbance regimes and the potential for resilience or irreversible tipping points in the face of change. Understanding the effects of disturbances such as storms, floods, and fires on post-disturbance recruitment can inform decisions about how key processes, structures, and interactions affect heterogeneity, diversity, and resilience over a range of spatial and temporal scales. Retention of structural legacies (dead and dying trees), mutualistic interactions (microbiotic soil crusts, mycorrhizal fungi), and key wild species (beavers) can promote biodiversity and carbon storage. Management of fire regimes, hydrological processes, and agricultural systems can promote carbon storage. However, difficult decisions about tradeoffs remain.
Edited by
Dan Chamberlain, University of Turin,Aleksi Lehikoinen, Finnish Museum of Natural History, University of Helsinki,Kathy Martin, University of British Columbia, Vancouver
Mountain areas have faced a rapid increase in human activities over recent decades, often leading to habitat loss or degradation. The impacts of these activities can affect bird species both directly (e.g., by altering habitat characteristics, impacting migration or disturbing breeding or wintering grounds), and indirectly by inducing physiological responses. We summarize the human activities that take place at high elevation and provide examples of species that are known to be impacted. Hiking and winter sports in particular are common in many mountain regions and there is growing evidence of a range of impacts on year-round resident mountain birds and their food resources. Increasing evidence also suggests that use of, and dependence on, human-derived foods around human settlements affects the trophic ecology of high-altitude birds. Hunting mountain birds is common place in many areas, and we review the evidence that hunting activity, including illegal persecution, has had impacts at the population level. Finally, we assess how direct disturbance and habitat alteration due to renewable energy developments (i.e. wind turbines and hydropower) are affecting mountain bird communities. There are many unknown impacts of human disturbance and we highlight missing information on specific topics that should be investigated in future research.
The climate benefit of forests is mostly recognized in their removal of carbon dioxide from the atmosphere. Over the course of a tree’s lifetime, the accumulated carbon in biomass is carbon removed from the atmosphere. Species differ in growth rate, size at maturity, and longevity, but the basic principle of biomass accumulation over the lifetime of a tree is the basis for using forests to remove carbon dioxide from the atmosphere. Decomposition of organic material in the soil emits carbon dioxide and reduces the net carbon gain by forests. Wildfires, insect outbreaks, logging, and other disturbances also release carbon dioxide to the atmosphere. The combination of these processes – carbon gain from biomass growth; carbon loss from the soil and from disturbances – makes some forests a sink for atmospheric carbon; the forests have a net gain of carbon annually. Other forests are a source of carbon, in which there is a net loss of carbon to the atmosphere. Forests are, at a global scale, an annual carbon sink, which reduces the accumulation of carbon dioxide in the atmosphere. Nature-based solutions to mitigate climate change aim to enhance the carbon sink.
Vultures are among the most threatened bird guilds on the planet and have a unique functional role within ecosystems. They are therefore subject to increasing research interest, calling for standardised study approaches and monitoring methods. The use of Unmanned Aircraft Systems (UASs) is rapidly gaining popularity in ecological research due to technological advances, affordability, and accessibility. This study reviews the existing peer-reviewed publications and grey literature on the responses of European vultures and other comparable species to UASs, and summarises the types of UAS use, their potential disturbance effects on vultures, and the resulting inter- and intra-specific interactions. Our goal was to assess the potential effects of UASs and to provide practical recommendations to optimise their safe use in vulture conservation and research. We acknowledge the potential of UASs to increase research efficiency and reduce research effort, time, and financial cost. Owing to the absence of sufficient data on long-term disturbance effects, we advocate the precautionary principle and offer a set of species-tailored practical recommendations to limit the potential negative effects of UASs and maximise their value in conservation management. We urge that the physiological and long-term impacts on vulture reproduction are considered and call for standardised monitoring protocols and controls on UAS use. Our conclusions and recommendations are particularly aimed at researchers working on vulture conservation and restoration projects worldwide.
Within two London parks, Richmond and Bushy, both subject to high public visitor pressure, behavioural observations were undertaken to investigate patterns of habitat use by red and fallow deer populations, and to determine the response of the deer to human disturbance. Potentially disturbing events were considered as: i. people present within a distance of < 50m; ii. people present within 50m accompanied by a dog on a lead; iii dogs within 50m off the lead; iv. people ‘crowding’ the deer - approaching directly and deliberately for photographs or closer observation; v. actual chases by a dog of the deer group or a member of that group.
All the above levels of disturbance caused a measurable change in the immediate behaviour patterns of the deer - reflected in increased levels of vigilance. Females responded more strongly than males of either species. However, the effects were relatively minor and transient in the great majority of cases, with animals resuming their normal activity very quickly after the encounter.
Overall daily time-budgets did not differ significantly between undisturbed days and days when disturbance levels were high; nor were any effects apparent on patterns of habitat use by the deer or in forcing the animals to change habitat more frequently. Further, throughout our studies there was no evidence that levels of disturbance caused by public access had any deleterious effects on body-weights or overwinter mortality.
A review of the literature was undertaken to consider the possible effects of human intervention (shepherding) at around the time of parturition in extensively farmed sheep. There is little clear empirical evidence to suggest that shepherding ensures either easy births or the integrity of ewe–lamb contact — factors closely linked to the welfare of the animals at this time. There is similarly no clear support for shepherding being harmful. However, the following suggestions are made: first, human presence can inhibit or delay parturition; second, extended parturition can increase the risk of, or is associated with, dystocia; and third, disturbance at birth can compromise ewe-lamb bonding and consequently lamb survival. Furthermore, sheep populations that have undergone rigorous selection for ease of lambing and minimal shepherding in extensive environments have well-documented physical and behavioural traits underlying their predisposition for enhanced lamb survival. Although our cultural legacy may impose a duty to intensively monitor animals at lambing, it is concluded that, at least in some situations, shepherding may not be entirely beneficial. The commonly held view of the necessity for some human intervention in extensive livestock systems is perhaps overly paternalistic, and requires a more comprehensive appraisal.
The Western Tragopan Tragopan melanocephalus is endemic to the Western Himalayas and currently listed as ‘Vulnerable’ on the IUCN Red List which also emphasizes a data deficiency regarding its distribution and population size. With this study we provide new data from the Palas Valley, northern Pakistan and deliver a range wide estimate of the species current, past, and future potential distribution as derived from environmental niche models. In the Palas Valley, Western Tragopans occupied different summer habitats on north-facing slopes and winter habitats on south-facing slopes. A quantitative estimate of local populations in six side valleys was inferred from individual call-count surveys during two breeding seasons (April and May 2017, 2018) and disturbance factors were evaluated from information of local people provided in questionnaires. Generalized-linear models (GLMs) showed a significant effect of disturbance factors on Western Tragopans, i.e. local abundances decreased with increasing disturbance from livestock, collectors and hunters visiting the area. This effect was visible across survey years and at both, south- as well as north-facing slopes. While the known distributional range of the Western Tragopan is small and fragmented, our niche models inferred climatically suitable space between Himachal Pradesh and northwestern Pakistan to be more continuous. Given the species sensitivity to disturbance, these findings indicate that the observed fragmentation of the current range might also be attributed to habitat transformation or anthropogenic disturbance rather than climatic suitability. During the Last Glacial Maximum (LGM) T. melanocephalus was probably restricted to small forest refugia, whereas projections onto eleven future climate simulations were inconclusive with the majority suggesting that climatically suitable space for T. melanocephalus will likely expand in response to anthropogenic climate change. In conclusion, we recommend that future conservation measures should be planned with regard to the species’ sensitivity to anthropogenic disturbances.
Three factors also related to impacts on wildlife are climate change, disease and disturbance. The UK has warmed significantly in recent decades, particularly in winter. This is having two main consequences for wildlife. Many plants and animals that reproduce in spring are doing so ever earlier. This phenological change has the potential to disturb food webs, although this does not yet seem to have happened to any significant extent. However, a second consequence, changes in species distributions, has certainly occurred. Many plants and animals have expanded northwards in Britain, and some newcomers have arrived from mainland Europe. On the downside, high alpine plants have declined and some seabirds have suffered from warming-related faunal changes in surrounding seas. Disease is a second factor that has caused some major species declines, including viral infections of rabbits and amphibians, as well as fungal mortality in trees. Finally, excessive disturbance by human footfall has generated environmental damage and at least local declines of sensitive species. This factor clearly relates to human numbers, but climate change is also influenced by the number of people on the planet as a whole.
Termites are essential components of tropical ecosystems, in which they provide fundamental ecosystem services, such as decomposition of dead plant material, fostering of soil mineralization and provisioning of new microhabitats. We investigated the termite communities of four habitats in two protected areas in West Africa, which differ in management effectiveness: the strictly protected Lamto Reserve (LR) and the Marahoué National Park (MNP), which suffers from anthropogenic disturbance despite its protection status. We tested the effect of disturbance on species composition, richness and abundance as well as on functional (feeding type) composition. The effect of disturbance was clearly visible in the termite communities. Compared to the LR, the MNP had less termite species overall and in all habitats except the shrub savannah. Also the abundance of termites was generally reduced and a decrease of soil feeders recorded. The latter is well-known to be sensitive to anthropogenic disturbance in forests. Comparing our results with other studies, we were able to identify suitable bioindicators of ecosystem health for West-African savannahs. Furthermore, we discuss the potential consequences of anthropogenic disturbance on ecosystem services provided by termites.
Invasive alien species are a major threat to global biodiversity due to the tremendous ecological and economic damage they cause in forestry, agriculture, wetlands, and pastoral resources. Understanding the spatial pattern of invasive alien species and disentangling the biophysical drivers of invasion at the forest stand level is essential for managing forest ecosystems and the wider landscape. However, forest-level and species-specific information on Invasive Alien Plant Species (IAPS) abundance and their spatial extent are largely lacking. In this context, we analysed the cover of one of the world’s worst invasive plants, Chromolaena odorata, in Sal (Shorea robusta) forest in central Nepal. Vegetation was sampled in four community forests using 0.01 ha square quadrats, covering the forest edge to the interior. C. odorata cover, floral richness, tree density, forest canopy cover, shrub cover, tree basal area, and disturbances were measured in each plot. We also explored forest and IAPS management practices in community forests. C. odorata cover was negatively correlated with forest canopy cover, distance to the road, angle of slope, and shrub cover. Tree canopy cover had the largest effect on C. odorata cover. No pattern of C. odorata cover was seen along native species richness gradients. In conclusion, forest canopy cover is the overriding biotic covariate suppressing C. odorata cover in Sal forests.