140 research outputs found

    Gaston Bachelard and Contemporary Philosophy

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    This special issue aims to redress the balance and to open up Gaston Bachelard's work beyond a small in-crowd of experts and aficionado’s in France. It aims to stimulate the discovery of new and understudied aspects of Bachelard’s work, including aspects of the intellectual milieu he was working in. Fortunately, for this purpose we were able to rely both on renowned Bachelard specialists, such as Hans-Jörg Rheinberg-er, Cristina Chimisso and Dominique Lecourt, as well as on a number of younger scholars who are discovering their work in a different intellectual context. At the same time we also want to reassess the value of this oeuvre, which also entails examining the reasons and causes of the relative neglect of Bachelard’s work in recent times. Has it exhausted its possibilities? Does it have intrinsic limitations that have contributed to the eclipse, as some influential, mainly French, philoso-phers have more or less explicitly suggested

    The curse of the black box

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    Predictability of plant-soil feedback

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    ABSTRACT In my thesis project I studied the role of soil biota as possible drivers of linkages between plant community diversity and plant productivity. My study was carried out in the framework of a large grassland biodiversity experiment in Jena, the so-called Jena Experiment. In chapter 1 I explain how soil biota may exert control over plant community productivity by recycling organic material and by intimately interacting with plant roots, either acting as antagonists to plants or as plant growth-promoting symbionts. Reciprocal interactions between plant and soil communities are an important component of so-called ‘plant-soil feedbacks’ (PSFs). In the PSF loop, plant community composition drives changes in belowground communities and abiotic conditions, which can subsequently alter plant community composition and productivity. Such PSF interactions have been proposed to play a major role in plant community composition and functioning. In the second chapter I review studies that use an experimental approach of inoculating live soils into sterilized background soils to study the effects of root symbionts on plant growth. I demonstrate that we make many assumptions when translating results of controlled studies to natural systems. I propose that we should continuously and carefully consider these assumptions and aim for rigid hypothesis testing by cross-talking between different levels of ecological realism. In chapter 3 I test how plant traits relate to PSF using a 49 grassland plant species of the Jena Experiment. First, I grew individuals of all species for two months in sterilized soil inoculated with field soil. In the subsequent feedback phase, I grew all plant species for 6 weeks in sterilized soil inoculated with (I) species-specific inoculum (conspecific conditioned soil), (II) sterilized species-specific inoculum, or (III) a mixture of all 49 species-specific inoculums (mixed conditioned soil). Subsequently I compared biomass production in conspecific conditioned soil to biomass production in sterilized soil (PSFsterilized) and in mixed conditioned soil (PSFmixed). Species with increasing specific root length (SRL) were increasingly susceptible to antagonistic interactions in conspecific conditioned soil (i.e. they had strong negative PSFsterilized), while thick-rooted plants had both positive PSFsterilized and high colonization rates of arbuscular mycorrhizal fungi (AMF). Finally, I showed that species ranking of PSFmixed was similar to species ranking of PSFsterilized, indicating that plants with increasingly negative net interactions in conspecific conditioned soil increasingly benefit from growing in mixed conditioned soil. With these findings, I made a first important step in placing PSFs in plant ecological strategy frameworks: high SRL is typical for plants that adopt a ‘fast’ growth strategy, characterized by fast resource acquisition but poor defense against antagonists and little reliance on AMF. In chapter 4, I test the relation between phylogenetic relatedness and the feedback effect of one (soil conditioning) plant species to another (responding) plant species. This is named indirect PSF. I grew eleven focal plant species, chosen to represent plants that had negative, neutral and positive PSFsterilized, in soils that were conditioned by conspecifics and soils conditioned by three to four other species with a varying degree of phylogenetic relatedness to the focal plant species. I found that plant species with negative PSF had no different or slightly better growth when growing in soil conditioned by plant species with larger phylogenetic distance to the focal plant. In contrast, plant species with neutral PSF grew less well, and species with positive PSF even worse, in soil conditioned by plant species with increasing phylogenetic distance to the focal plant. I conclude that the effect of phylogenetic relatedness on PSF interactions between plant species may depend on the tendency of the focal plant species to develop detrimental or beneficial interactions with soil microbes. In chapter 5, I use the PSFmixed values of chapter 3 in a correlational analysis to test how short-term PSFs relate to longer-term species’ performances in the field, using established monocultures and species-rich (60 species) plant communities of the Jena Experiment. Based on some recently published studies I expected that plants with more negative PSFmixed would benefit most from growing in mixtures; these plant species were expected to overyield most in mixed plant communities. However, opposite to the expectation, plant species with the most negative PSF produced least biomass in the 60-species plant communities, whereas plant performance in monoculture was not related to its short-term PSF. I conclude that species-specific overyielding was positively related to species-specific PSF, and that community overyielding was mostly driven by plant species with a neutral to positive PSF. Finally, in chapter 6 I examine the role of quality and quantity of plant biomass in driving nematode feeding group abundance and diversity. I found strong positive effects of both plant species- and plant functional group-richness on abundances of plant feeding, bacterial feeding and fungal feeding nematodes, as well as omnivores, but not for predators. Structural equation modeling (SEM) analysis showed that the positive effect of plant diversity on the abundance of microbial feeding nematodes (fungal plus bacterial feeders) could not be explained by increased microbial biomass. Similarly, the abundance of plant feeding nematodes was not driven by the higher plant biomass in species rich plant communities. Instead, increased plant biomass explained the positive relation between plant species richness and the abundance of microbial feeding nematodes, while for plant feeding nematodes, increased C to N ratio of aboveground plant biomass appeared to explain the positive relation between the abundance of plant feeding nematodes and plant species and functional group richness. Importantly, the density of plant feeding nematodes per unit root biomass decreased with increasing plant diversity, indicating a root feeder dilution effect. I conclude that plant diversity does not explain nematode community composition primarily by simple bottom-up relations, but that other aspects, such as quality of resource and microhabitats quality, may play a role as well.</p

    The strength of negative plant–soil feedback increases from the intraspecific to the interspecific and the functional group level

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    One of the processes that may play a key role in plant species coexistence and ecosystem functioning is plant–soil feedback, the effect of plants on associated soil communities and the resulting feedback on plant performance. Plant–soil feedback at the interspecific level (comparing growth on own soil with growth on soil from different species) has been studied extensively, while plant–soil feedback at the intraspecific level (comparing growth on own soil with growth on soil from different accessions within a species) has only recently gained attention. Very few studies have investigated the direction and strength of feedback among different taxonomic levels, and initial results have been inconclusive, discussing phylogeny, and morphology as possible determinants. To test our hypotheses that the strength of negative feedback on plant performance increases with increasing taxonomic level and that this relationship is explained by morphological similarities, we conducted a greenhouse experiment using species assigned to three taxonomic levels (intraspecific, interspecific, and functional group level). We measured certain fitness‐related aboveground traits and used them along literature‐derived traits to determine the influence of morphological similarities on the strength and direction of the feedback. We found that the average strength of negative feedback increased from the intraspecific over the interspecific to the functional group level. However, individual accessions and species differed in the direction and strength of the feedback. None of our results could be explained by morphological dissimilarities or individual traits. Synthesis. Our results indicate that negative plant–soil feedback is stronger if the involved plants belong to more distantly related species. We conclude that the taxonomic level is an important factor in the maintenance of plant coexistence with plant–soil feedback as a potential stabilizing mechanism and should be addressed explicitly in coexistence research, while the traits considered here seem to play a minor role

    Food, Nutrition and Agrobiodiversity Under Global Climate Change

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    Available evidence and predictions suggest overall negative effects on agricultural production as a result of climate change, especially when more food is required by a growing population. Information on the effects of global warming on pests and pathogens affecting agricultural crops is limited, though crop–pest models could offer means to predict changes in pest dynamics, and help design sound plant health management practices. Host-plant resistance should continue to receive high priority as global warming may favor emergence of new pest epidemics. There is increased risk, due to climate change, to food and feed contaminated by mycotoxin-producing fungi. Mycotoxin biosynthesis gene-specific microarray is being used to identify food-born fungi and associated mycotoxins, and investigate the influence of environmental parameters and their interactions for control of mycotoxin in food crops. Some crop wild relatives are threatened plant species and efforts should be made for their in situ conservation to ensure evolution of new variants, which may contribute to addressing new challenges to agricultural production. There should be more emphasis on germplasm enhancement to develop intermediate products with specific characteristics to support plant breeding. Abiotic stress response is routinely dissected to component physiological traits. Use of transgene(s) has led to the development of transgenic events, which could provide enhanced adaptation to abiotic stresses that are exacerbated by climate change. Global warming is also associated with declining nutritional quality of food crops. Micronutrient-dense cultivars have been released in selected areas of the developing world, while various nutritionally enhanced lines are in the release pipeline. The high-throughput phenomic platforms are allowing researchers to accurately measure plant growth and development, analyze nutritional traits, and assess response to stresses on large sets of individuals. Analogs for tomorrow’s agriculture offer a virtual natural laboratory to innovate and test technological options to develop climate resilience production systems. Increased use of agrobiodiversity is crucial to coping with adverse impacts of global warming on food and feed production and quality. No one solution will suffice to adapt to climate change and its variability. Suits of technological innovations, including climate-resilient crop cultivars, will be needed to feed 9 billion people who will be living in the Earth by the middle of the twenty-first century
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