No abstract is provided for this article.
Alterations in fire activity due to climate change and fire suppression may have profound effects on the balance between storage and release of carbon (C) and associated volatile elements. Stored soil mercury (Hg) is known to volatilize due to wildfires and this could substantially affect the land-air exchange of Hg; conversely the absence of fires and human disturbance may increase the time period over which Hg is sequestered. Here we show for a wildfire chronosequence spanning over more than 5000 years in boreal forest in northern Sweden that belowground inventories of total Hg are strongly related to soil humus C accumulation (R2 = 0.94, p < 0.001). Our data clearly show that northern boreal forest soils have a strong sink capacity for Hg, and indicate that the sequestered Hg is bound in soil organic matter pools accumulating over millennia. Our results also suggest that more than half of the Hg stock in the sites with the longest time since fire originates from deposition predating the onset of large-scale anthropogenic emissions. This study emphasizes the importance of boreal forest humus soils for Hg storage and reveals that this pool is likely to persist over millennial time scales in the prolonged absence of fire.
All communities and ecosystems are subjected to a range of extrinsic factors that can be broadly classified as stress factors (i.e. those that remain constantly limiting for organism growth and do not change markedly over time) and disturbance factors (i.e. those that involve rapid changes and often involve destruction of organism biomass). Although the interactive effects between stress and disturbance have been well explored for plant communities, little is known about how these interactions influence soil communities. We set up a 14-month glasshouse experiment, which consisted of varying levels of a disturbance (plant defoliation) and a stress (gradient of water limitation to plants), in a full factorial design. Response variables consisted of plant biomass and productivity, soil microbial biomass and activity (measured using multiple substrate utilization profiling), and soil microbial community structure (measured using phospholipid fatty acid analysis). Although the microbial community responded to both the stress and disturbance factors, these responses did not closely track plant responses to the same factors, pointing to a degree of decoupling between plant and microbial communities. Further, although stress and disturbance factors both limited some measures of microbial biomass and activity, the microbial community responded to these two factors in quite different ways. There were no interactive effects of stress and disturbance on any microbial response variables, with the exception of one variable that involved total microbial community substrate utilization. Although the ability of microbes to exploit water resources that are less available to plants may buffer the soil microbial community from stress, the general lack of interactions of stress and disturbance on the microbial community contrasts with what has been shown for plant communities and proposed for fungal communities. Our results suggest that while stress and disturbance are both strong drivers of the microbial community, the effects of these factors largely operate independently from one another.
No abstract is provided for this article.
While several studies have explored how short-term ecological responses to disturbance vary among ecosystems, experimental studies of how contrasting ecosystems recover from disturbance in the longer term are few. We performed a simple long-term experiment on each of 30 contrasting forested islands in northern Sweden that vary in size; as size decreases, time since fire increases, soil fertility and ecosystem productivity declines, and plant species diversity increases. We predicted that resilience of understory plant community properties would be greatest on the larger, more productive islands, and that this would be paralleled by greater resilience of soil biotic and abiotic properties. For each island, we applied three disturbance treatments of increasing intensity to the forest understory once in 1998, i.e., light trimming, heavy trimming, and burning; a fourth treatment was an undisturbed control. We measured recovery of the understory vascular plant community annually over the following 14 years, and at that time also assessed recovery of mosses and several belowground variables. Consistent with our predictions, vascular plant whole-community variables (total cover, species richness, diversity [Shannon's H'], and community composition) recovered significantly more slowly on the smaller (least fertile) than the larger islands, but this difference was not substantial, and only noticeable in the most severely disturbed treatment. When an index of resilience was used, we were unable to detect effects of island size on the recovery of any property. We found that mosses and one shrub species (Empetrum hermaphroditum) recovered particularly slowly, and the higher abundance of this shrub on small islands was sufficient to explain any slower recovery of whole-ecosystem variables on those islands. Further, several belowground variables had not fully recovered from the most intense disturbance after 14 yr, and counter to our predictions, the degree of their recovery was never influenced by island size. While several studies have shown large variation among plant communities in their short-term response (notably resistance) to environmental perturbations, our results reveal that when perturbations are applied equally to highly contrasting ecosystems, differences in resilience among them in the longer term can be relatively minor, regardless of the severity of disturbance.
No abstract is provided for this article.
Allelopathy is an interference mechanism by which plants release chemicals which affect other plants; while it has often been proposed as a mechanism for influencing plant populations and communities, its acceptance by plant ecologists has been limited because of methodological problems as well as difficulties of relating the results of bioassays used for testing allelopathy to vegetation patterns in the field. Here we argue that the concept of allelopathy is more appropriately applied at the ecosystem‐level, rather than the traditional population/community level of resolution. Firstly, we consider the wide ranging effects of secondary metabolites (widely regarded as allelochemicals) on organisms and processes which regulate ecosystem function, including herbivory, decomposition and nutrient mineralization. It is apparent that plants with allelopathic potential against other organisms induce net changes in ecosystem properties, which may in turn impact upon the plant community in the longer term. We then illustrate these concepts using two contrasting examples of how invasive plant species with allelopathic potential may alter ecosystem properties through the production of secondary metabolites, i.e. Carduus nutans (nodding thistle) in New Zealand pastures and Empetrum hermaphroditum (crowberry) in Swedish boreal forests. In both cases the production of secondary metabolites by the invasive species induces important effects on other organisms and key processes, which help determine how the ecosystem functions and ultimately the structure of the plant community. These examples help demonstrate that the concept of allelopathy is most effectively applied at the ecosystem‐level of resolution, rather than at the population‐level (i.e. plant‐plant interference).
Some communities are susceptible to invasions and some are not. Why? Elton suggested in 1958 that the ability of the community to withstand invading species – its biotic resistance – depends on the number of resident species. Later contributors have emphasized the habitat's ability to support species, as well as the contribution of individual species to the resistance. In this study we use information from 184 introductions of Arctic char into Swedish lakes to study both abiotic and biotic aspects of the resident community's ability to resist introductions. We find that the best model included the proportion of forest cover and the proportion of agricultural land cover in the watershed in combination with the presence versus absence of northern pike. Thus, the most important biotic factor to explain the outcome of introductions of Arctic char is the presence of northern pike, a large piscivore. This means that one single species explains the outcome of the introductions better than does the species richness or the saturation level of the community.
While there has been a rapidly increasing research effort focused on understanding whether and how composition and richness of species and functional groups may determine ecosystem properties, much remains unknown about how these community attributes affect the dynamic properties of ecosystems. We conducted an experiment in 540 mini‐ecosystems in glasshouse conditions, using an experimental design previously shown to be appropriate for testing for functional group richness and composition effects in ecosystems. Artificial communities representing 12 different above‐ground community structures were assembled. These included treatments consisting of monoculture and two‐ and four‐species mixtures from a pool of four plant species; each plant species represented a different functional group. Additional treatments included two herbivore species, either singly or in mixture, and with or without top predators. These experimental units were then either subjected to an experimentally imposed disturbance (drought) for 40 d or left undisturbed. Community composition and drought both had important effects on plant productivity and biomass, and on several below‐ground chemical and biological properties, including those linked to the functioning of the decomposer subsystem. Many of these compositional effects were due to effects both of plant and of herbivore species. Plant functional group richness also exerted positive effects on plant biomass and productivity, but not on any of the below‐ground properties. Above‐ground composition also had important effects on the response of below‐ground properties to drought and thus influenced ecosystem stability (resistance); effects of composition on drought resistance of above‐ground plant response variables and soil chemical properties were weaker and less consistent. Despite the positive effects of plant functional group richness on some ecosystem properties, there was no effect of richness on the resistance of any of the ecosystem properties we considered. Although herbivores had detectable effects on the resistance of some ecosystem properties, there were no effects of the mixed herbivore species treatment on resistance relative to the single species herbivore treatments. Increasing above‐ground food chain length from zero to three trophic levels did not have any consistent effect on the stability of ecosystem properties. There was no evidence of either above‐ground composition or functional group richness affecting the recovery rate of ecosystem properties from drought and hence ecosystem resilience. Our data collectively point to the role of composition (identity of functional group), but not functional group richness, in determining the stability (resistance to disturbance) of ecosystem properties, and indicates that the nature of the above‐ground community can be an important determinant of the consistency of delivery of ecosystem services.
Summary: Résumé: Zusammenfassung The allelopathic influence of four developmental stages of nodding thistle (small rosette, large rosette, bolting and dead plants) on eleven test species (six grasses, four legumes and itself) was investigated using aqueous extract bioassays, aqueous leachate bioassays, and bioassays based on addition of ground material to soil. The aqueous extract and leachate bioassays indicated that nodding thistle was most allelopathic at the rosette stages, while the bioassays involving amendment of soil with thistle tissue showed bolting live and dead plants to be the most allelopathic. It is proposed that nodding thistle is allelopathic at two phases of its development, i.e. at the early bolting stage when the larger rosette leaves are decomposing and releasing soluble inhibitors, and at the stage when bolting plants are dying and releasing insoluble inhibitors. Nodding thistle seedlings appear to be stimulated by addition of thistle tissues to soil, indicating that thistle plants may weaken pasture and simultaneously encourage recruitment of its own species. This is consistent with previous studies detecting high densities of thistle seedlings in the vicinity of deceased parent plants. The six grass species were generally more tolerant to thistle allelopathic effects than were the four legume species, but no consistent differences emerged between different grass or legume species. Influence de l'age de la plante sur le potentiel allélopathique du chardon penche (Carduus nutans L. ) vis a vis des prairies de graminées et de légumineuses L'influence allélopathique de 4 stades de développement du chardon penché (petite rosette, grande rosette, montaison, plantes mortes) sur 11 espèces tests (6 graminées, 4 légumineuses et lui‐même) a étéétudiée en utilisant des bioessais d'extraction acqueuse, des bioessais de lessivage acqueux et des bioessais fondés sur l'addition au sol d'amendement. Les bioessais d'extraction acqueuse et de lessivage ont montré que le chardon penchéétait plus allélopathique au stade rosette tandis que les bioessais impliquant l'amendement de sol avec des tissues de chardon ont montré que la montaison et les plantes mortes étaient les plus allélopathiques. Il est proposé que le chardon penché est allélopathique à 2 phases de son développement, par exemple au stade montaison précoce quand les plus grandes feuilles de la rosette se décomposent et relachent les inhibiteurs solubles, et au stade où les plantes montées meurent et relächent les inhibiteurs insolubles. Les plantules de chardon penché apparaissent être stimulées par l'addition de tissus de chardon au sol, montrant que les plantes de chardon peuvent affaiblir une prairie et simultanément favoriser sa propre réimplantation. Ceci est conforme avec des études précédentes montrant des fortes densités de plantules de chardon au voisinage de plantes parentes mortes. Les 6 espèces de graminées ont été de façon générale plus tolérantes aux effets allélopathiques que les 4 espèces de légumineuses, mais aucune différence importante ne s'est exprimée entre les différentes espèces de graminées ou de légumineuses. Einfluβ des Pflanzenalters der Nickenden Distel (Carduus nutans L.) auf die allelopathische Wirkung gegen Weidegräser und Leguminosen Die allelopathische Wirkung der Nickenden Distel wurde in 4 Entwicklungsstadien (in kleiner und in voller Rosette, blütentreibend und abgestorben) gegen 11 Pflanzenarten (6 Gräser, 5 Leguminosen und sich selbst) mit wäßrigen Auszügen, Perkolationswasser und Bodenmaterial zum Substrat geprüft. Mit den wäßrigen Auszügen und dem Perkolationswasser zeigte sich die Nickende Distel im Rosetten‐Stadium am meisten allelopathisch, während Bodenmaterial mit Resten blütentreibender und abgestorbener Pflanzen wirksamer war. Es kann angenommen werden, daß die Nickende Distel in 2 Entwicklung sphasen allelopathisch wirkt, nämlich wenn die größeren Rosettenblätter oder wenn die blütentreibenden Pflanzen vergeben und 1ösliche Hemmstoffe entlassen. Keimpflanzen der Nickenden Distel werden offensichtlich durch Pflanzenmaterial der Distel im Wachstum angeregt; die Distel schwächt also Weide‐Pflanzenarten und fördert zugleich ihre eigene Entwicklung. Dieser Befund deckt sich mit der Beobachtung hoher Keimpflanzen‐Dichten um abgestorbenen Mutterpflanzen. Die 6 Gräser waren durchweg gegenüber der allelopathischen Wirkung der Distel unempfindlicher als die 4 Leguminosen, doch innerhalb dieser Gruppen zeigten sich keine klaren Unterschiede.
The role of interspecific competition in fungal communities in natural substrates is poorly understood because fungi do not form easily definable populatio
Forest dwelling browsing mammals, notably feral goats and deer, have been introduced to New Zealand over the past 220 years; prior to this such mammals were absent from New Zealand. The New Zealand forested landscape, therefore, presents an almost unique opportunity to determine the impacts of introduction of an entire functional group of alien animals to a habitat from which that group was previously absent. We sampled 30 long-term fenced exclosure plots in indigenous forests throughout New Zealand to evaluate community- and ecosystem-level impacts of introduced browsing mammals, emphasizing the decomposer subsystem. Browsing mammals often significantly altered plant community composition, reducing palatable broad-leaved species and promoting other less palatable types. Vegetation density in the browse layer was also usually reduced. Although there were some small but statistically significant effects of browsing on some measures of soil quality across the 30 locations, there were no consistent effects on components of the soil microfood web (comprising microflora and nematodes, and spanning three consumer trophic levels); while there were clear multitrophic effects of browsing on this food web for several locations, comparable numbers of locations showed stimulation and inhibition of biomasses or populations of food web components. In contrast, all microarthropod and macrofaunal groups were consistently adversely affected by browsing, irrespective of trophic position. Across the 30 locations, the magnitude of response of the dominant soil biotic groups to browsing mammals (and hence their resistance to browsers) was not correlated with the magnitude of vegetation response to browsing but was often strongly related to a range of other variables, including macroclimatic, soil nutrient, and tree stand properties. There were often strong significant effects of browsing mammals on species composition of the plant community, species composition of leaf litter in the litter layer, and composition of various litter-dwelling faunal groups. Across the 30 locations, the magnitude of browsing mammal effects on faunal community composition was often correlated with browser effects on litter layer leaf species composition but never with browser effects on plant community composition. Browsing mammals usually reduced browse layer plant diversity and often also altered habitat diversity in the litter layer and diversity of various soil faunal groups. Across the 30 locations, the magnitude of browser effects on diversity of only one faunal group, humus-dwelling nematodes, was correlated with browser effects on plant diversity. However, browser effects on diversity of diplopods and gastropods were correlated with browser effects on habitat diversity of the litter layer. Reasons for the lack of unidirectional relationships across locations between effects of browsers on vegetation community attributes and on soil invertebrate community attributes are discussed. Browsing mammals generally did not have strong effects on C mineralization but did significantly influence soil C and N storage on an areal basis for several locations. However the direction of these effects was idiosyncratic and presumably reflects different mechanisms by which browsers affect soil processes. While our study did not support hypotheses predicting consistent negative effects of browsing mammals on the decomposer subsystem through promotion of plant species with poorer litter quality, our results still show that the introduction of these mammals to New Zealand has caused far-ranging effects at both the community and ecosystem levels of resolution, with particularly adverse effects for indigenous plant communities and populations of most groups of litter-dwelling mesofauna and macrofauna.
1. A study on the interactions between Carduus nutans L. (nodding thistle), and pasture grasses and legumes was conducted in a New Zealand perennial pasture. 3.8 × 3.8 m plots were sown with each of 10 forage species (six grasses and four legumes), or maintained free of pasture (bare ground plots). A 2 × 1 m subplot was established in each plot in which total thistle seedling emergence and pasture species composition were assessed over a 26-month period; in the remainder of each plot 10 thistles were labelled and monitored for subsequent growth rate, development and survivorship. 2. Thistle seedling emergence was greater in some of the legume-sown treatments than in the grass-sown treatments for the first few months of the study. Seedling emergence was negatively related to sown grass cover and the cover of volunteer Poa annua L. in the plots. However, seedling emergence in the bare ground plots was often substantially less than for the other treatments, probably because at least some pasture cover was necessary to provide an adequate microclimate for establishment. 3. The preflowering mortality of thistles was lowest in the bare-ground treatment, intermediate in the legume-sown treatments and highest in the grass-sown treatments. All thistles which survived to flowering in the bare-ground and legume plots behaved as annuals, while between 3 and 16% of thistles in the various grass-sown plots continued into their second year as rosettes, and many of these flowered as biennials. Preflowering thistle mortality was strongly related to the grass (including P. annua) content of the plots. 4. Flowering thistles in the bare ground plots grew larger than in the sown plots and produced substantially more capitula. Generally, the thistles in the legumesown plots also grew larger than those in the grass-sown plots. 5. Grass-sown plots were likely to be invaded by P. annua in the first few months following sowing, while the legume-sown plots tended to be invaded by broadleaved weeds. The sown grass ― P. annua associations appear to be substantially more effective than the sown legume ― broadleaved weed associations in reducing the problem of nodding thistle invasions
