Jasmin Joshi

Ecosystem effects of biodiversity manipulations in European grasslands.

We present a multisite analysis of the relationship between plant diversity and ecosystem functioning within the European BIODEPTH network of plant-diversity manipulation experiments. We report results of the analysis of 11 variables addressing several aspects of key ecosystem processes like biomass production, resource use (space, light, and nitrogen), and decomposition, measured across three years in plots of varying plant species richness at eight different European grassland field sites. Differences among sites explained substantial and significant amounts of the variation of most of the ecosystem processes examined. However, against this background of geographic variation, all the aspects of plant diversity and composition we examined (i.e., both numbers and types of species and functional groups) produced significant, mostly positive impacts on ecosystem processes. Analyses using the additive partitioning method revealed that complementarity effects (greater net yields than predicted from monocultures due to resource partitioning, positive interactions, etc.) were stronger and more consistent than selection effects (the covariance between monoculture yield and change in yield in mixtures) caused by dominance of species with particular traits. In general, communities with a higher diversity of species and functional groups were more productive and utilized resources more completely by intercepting more light, taking up more nitrogen, and occupying more of the available space. Diversity had significant effects through both increased vegetation cover and greater nitrogen retention by plants when this resource was more abundant through N2 fixation by legumes. However, additional positive diversity effects remained even after controlling for differences in vegetation cover and for the presence of legumes in communities. Diversity effects were stronger on above- than belowground processes. In particular, clear diversity effects on decomposition were only observed at one of the eight sites. The ecosystem effects of plant diversity also varied between sites and years. In general, diversity effects were lowest in the first year and stronger later in the experiment, indicating that they were not transitional due to community establishment. These analyses of our complete ecosystem process data set largely reinforce our previous results, and those from comparable biodiversity experiments, and extend the generality of diversity–ecosystem functioning relationships to multiple sites, years, and processes.

Numerical responses of different trophic groups of invertebrates to manipulations of plant diversity in grasslands.

Abstract. We studied the effects of plant diversity on abundance of invertebrate herbivores, parasitoids and predators in two grassland communities (one in Switzerland and one in Sweden) in which plant species richness and functional diversity have been experimentally manipulated. Among herbivores, the abundance of only the most sessile and specialised groups (leafhoppers and wingless aphids) was affected by plant diversity. At both sites, numbers of leafhoppers in sweep net samples showed a linear, negative relationship with plant species number whereas numbers of wingless aphids in suction samples increased with the number of plant functional groups (grasses, legumes, and non-legume forbs) present in the plot. Activity of carabid beetles and spiders (as revealed by pitfall catches) and the total number of predators in pitfalls at the Swiss site decreased linearly with increases in the number of plant species and plant functional groups. Abundance of more specialised enemies, hymenopteran parasitoids, was not affected by the manipulations of plant diversity. Path analysis and analysis of covariance indicated that plant diversity effects on invertebrate abundance were mostly indirect and mediated by changes in plant biomass and cover. At both sites, plant species composition (i.e. the identity of plant species in a mixture) affected numbers of most of the examined groups of invertebrates and was, therefore, a more important determinant of invertebrate abundance in grasslands than plant species richness per se or the number of plant functional groups. The presence of legumes in a mixture was especially important and led to higher numbers of most invertebrate groups. The similarity of invertebrate responses to plant diversity at the two study sites indicates that general patterns in abundance of different trophic groups can be detected across plant diversity gradients under different environmental conditions.

Rapid decay of diversity-productivity relationships after invasion of experimental plant communities

Abstract So far, effects of species richness on ecosystem functioning have mainly been investigated in the short term in experimental communities from which invasion was prevented. We kept the local species pools of experimental grassland communities with 1, 2, 4, 8, and 32 species closed for five years and subsequently opened them for invasion by cessation of weeding. As long as communities were weeded, extinctions were rare but positively related to species richness, diversity-productivity relationships were positive, and more diverse systems had a greater temporal stability. Following cessation of weeding, species-poor communities were more prone to invasion. However, invasion increased extinction especially in species-rich communities. Within two years, differences in species richness and biomass production between sets of communities of different initial species richness disappeared and the positive diversity-productivity relationship was no longer detectable whereas species compositions remained distinct. This indicates that the positive diversity-productivity relationships during the weeding phase were mainly controlled by species richness. Bis anhin wurden die Effekte der Artenvielfalt auf das Funktionieren von Okosystemen vor allem in kurzfristigen Experimenten untersucht, in denen die Einwanderung von Pflanzenarten in die bestehenden Gesellschaften verhindert wurde. Im vorliegenden Versuch wurden die lokalen Artenpools von 1, 2, 4, 8 und 32 Arten unserer experimentellen Graslandgesellschaften wahrend 5 Jahren kunstlich geschlossen gehalten und danach geoffnet indem nicht mehr gejatet wurde. Solange die Gesellschaften gejatet wurden, gab es wenige Aussterbeereignisse, die aber positiv mit der Artenvielfalt korreliert waren. Die Beziehung zwischen Diversitat und Produktivitat war positiv und Systeme hoherer Diversitat zeigten eine grosere zeitliche Stabilitat. Nach der Aufgabe des Jatens nahm die Einwanderung vor allem in artenarmen Gesellschaften zu. Die Einwanderung erhohte jedoch besonders das Aussterben in ursprunglich artenreichen Gesellschaften. Innerhalb von zwei Jahren verschwanden die Unterschiede in der Artenzahl und Biomasseproduktion zwischen den verschiedenen Graslandgesellschaften und eine positive Beziehung zwischen Diversitat und Produktivitat war nicht mehr feststellbar. Die Artenzusammensetzung der Versuchsflachen blieb jedoch unterschiedlich. Das deutet darauf hin, das die positive Beziehung zwischen Diversitat und Produktivitat wahrend der ersten Phase des Experiments vor allem durch die Artenzahl und nicht durch die Artenzusammensetzung hervorgerufen wurde.

Conservation implications of the link between biodiversity and ecosystem functioning

The relationship between biodiversity and individual ecosystem processes is often asymptotic, saturating at relatively low levels, with some species contributing more strongly than others. This has cast doubt on arguments for conservation based on maintenance of the functioning of ecosystems. However, we argue that the link between biodiversity and ecosystem functioning is an important additional argument for conservation for several reasons. (1) Although species differ in importance to ecosystem processes, we do not believe that this argues for preservation of just a few species for two reasons: first, it is nearly impossible to identify all species important to the numerous systems and processes on which humans depend; second, the important species themselves may depend on an unknown number of other species in their communities. (2) Arguments for conservation based on ecosystem functioning are complementary to other utilitarian, ethical and aesthetic justifications. No single reason will convince all people or protect all species, however the combination produces a strong case for conservation of biodiversity. (3) Even if the relationship between biodiversity and ecosystem functioning is asymptotic at local spatial scales and in the short term, effects of biodiversity loss are likely to be important at larger temporal and spatial scales. (4) Initial arguments for the importance of biodiversity for ecosystem functioning were largely based on a precautionary approach (points 1–3). However, we are now moving to a scientific position based on accumulating experimental evidence. The future challenge is the integration of this scientific research with policy.

Species richness, but not phylogenetic diversity, influences community biomass production and temporal stability in a re-examination of 16 grassland biodiversity studies

Summary 1. Hundreds of experiments have now manipulated species richness (SR) of various groups of organisms and examined how this aspect of biological diversity influences ecosystem functioning. Ecologists have recently expanded this field to look at whether phylogenetic diversity (PD) among species, often quantified as the sum of branch lengths on a molecular phylogeny leading to all species in a community, also predicts ecological function. Some have hypothesized that phylogenetic divergence should be a superior predictor of ecological function than SR because evolutionary relatedness represents the degree of ecological and functional differentiation among species. But studies to date have provided mixed support for this hypothesis. 2. Here, we reanalyse data from 16 experiments that have manipulated plant SR in grassland ecosystems and examined the impact on above-ground biomass production over multiple time points. Using a new molecular phylogeny of the plant species used in these experiments, we quantified how the PD of plants impacts average community biomass production as well as the stability of community biomass production through time. 3. Using four complementary analyses, we show that, after statistically controlling for variation in SR, PD (the sum of branches in a molecular phylogenetic tree connecting all species in a community) is neither related to mean community biomass nor to the temporal stability of biomass. These results run counter to past claims. However, after controlling for SR, PD was

The functioning of European grassland ecosystems: Potential benefits of biodiversity to agriculture

About half the farmland of Europe is grassland pasture or hay meadow, and much is impoverished in plant species due to the addition of fertilizers and pesticides, agricultural re-sowing, habitat fragmentation, land abandonment and changes in grazing and mowing regimes. Given this widespread reduction, it is important to understand the effect that loss of biodiversity is having upon our wider environment. Here the authors summarize the main results from the BIODEPTH project, the first multinational, large-scale experiment to examine directly the relationship between plant diversity and the processes that determine the functioning of ecosystems. The results suggest that preserving and restoring grassland diversity may be beneficial to maintaining desirable levels of several ecosystem processes, and may therefore have applications in land management and agriculture.

Increased frequency of scale anomalies and loss of genetic variation in serially bottlenecked populations of the dice snake, Natrix tessellata

Documented demographic bottlenecks resultingfrom introductions of the dice snake to severallakes in Switzerland provide a rare opportunityto study the effect of serial bottlenecks onthe genetic properties of Natrixtessellata populations. We investigated twointroduced populations using informationderived from eight microsatellite markers. Bothintroduced populations had significantlyreduced levels of allelic diversity relative tonon-bottlenecked populations. The severity ofthe bottlenecks was underlined by thesignificant reduction in observed and expectedheterozygosity. The loss of allelic diversityand observed heterozygosity was stronger in theserially bottlenecked population than in thepopulation that was bottlenecked only once.From previous studies, scale anomalies wereknown to be more common in introducedpopulations relative to native populations. Weinvestigated whether the higher occurrence ofscale anomalies in introduced populations isassociated with individual heterozygosity andmean genomic diversity d2. We founda significant relationship between theoccurrence of scale anomalies and individualheterozygosity but no significant relationshipbetween scale anomalies and the microsatellitespecific measurement, d2, was found.Because of their known history, introducedpopulations in Switzerland may serve as a modelto demonstrate the effect of severe populationbottlenecks on genetic variability anddevelopmental stability in N. tessellata.The results therefore help to device strategiesfor the management and protection of endangerednatural N. tessellata populations.

In their native range, invasive plants are held in check by negative soil-feedbacks.

The ability of some plant species to dominate communities in new biogeographical ranges has been attributed to an innate higher competitive ability and release from co-evolved specialist enemies. Specifically, invasive success in the new range might be explained by release from biotic negative soil-feedbacks, which control potentially dominant species in their native range. To test this hypothesis, we grew individuals from sixteen phylogenetically paired European grassland species that became either invasive or naturalized in new ranges, in either sterilized soil or in sterilized soil with unsterilized soil inoculum from their native home range. We found that although the native members of invasive species generally performed better than those of naturalized species, these native members of invasive species also responded more negatively to native soil inoculum than did the native members of naturalized species. This supports our hypothesis that potentially invasive species in their native range are held in check by negative soil-feedbacks. However, contrary to expectation, negative soil-feedbacks in potentially invasive species were not much increased by interspecific competition. There was no significant variation among families between invasive and naturalized species regarding their feedback response (negative vs. neutral). Therefore, we conclude that the observed negative soil feedbacks in potentially invasive species may be quite widespread in European families of typical grassland species.

Plant-soil feedbacks: a comparative study on the relative importance of soil feedbacks in the greenhouse versus the field

Interactions between plants and soil microorganisms influence individual plant performance and thus plant-community composition. Most studies on such plant-soil feedbacks (PSFs) have been performed under controlled greenhouse conditions, whereas no study has directly compared PSFs under greenhouse and natural field conditions. We grew three grass species that differ in local abundance in grassland communities simultaneously in the greenhouse and field on field-collected soils either previously conditioned by these species or by the general grassland community. As soils in grasslands are typically conditioned by mixes of species through the patchy and heterogeneous plant species’ distributions, we additionally compared the effects of species-specific versus non-specific species conditioning on PSFs in natural and greenhouse conditions. In almost all comparisons PSFs differed between the greenhouse and field. In the greenhouse, plant growth in species-specific and non-specific soils resulted in similar effects with neutral PSFs for the most abundant species and positive PSFs for the less abundant species. In contrast, in the field all grass species tested performed best in non-specific plots, whereas species-specific PSFs were neutral for the most abundant and varied for the less abundant species. This indicates a general beneficial effect of plant diversity on PSFs in the field. Controlled greenhouse conditions might provide valuable insights on the nominal effects of soils on plants. However, the PSFs observed in greenhouse conditions may not be the determining drivers in natural plant communities where their effects may be overwhelmed by the diversity of abiotic and biotic above- and belowground interactions in the field.

Entrepreneurship in biodiversity conservation and regional development

This paper discusses the protection of biodiversity by means of market-based activities in the food sector and the preconditions and context that provide fertile ground. The variables investigated are the regional production factors involved, the entrepreneurship demonstrated, the kind of niche market developed, and the various kinds of support provided. A case study of a Swiss market activity designed to restore and protect biodiversity is presented; it concerns the cultivation of a traditionally grown wheat species combined with measures to protect wildlife and flora. The wheat is processed into a variety of products, which are sold within the region. The organization of the activity, its economic development and its ecological implications are presented. The discussion reveals the particularities of such endeavours that are of relevance to the economics of regional development (e.g. limited product and market development, reliance on subsidies, need for broad coalitions) and factors of success (e.g. networking, involvement of research, political support). Conclusions with regard to policy are as follows: (1) support in the very early stages is needed (e.g. start-up capital, capacity building, partner-like support from administration); (2) biodiversity-sound agricultural activities rely on subsidies; and (3) a propitious framework for such market activities is to be conserved.