Abstract:1. Forest structure and diversity can regulate tree vulnerability to damage by insects and pathogens. Past work suggests that trees with diverse neighbours should experience less leaf herbivory and less damage from specialist herbivores and diseases, and that the effect of neighbourhood diversity should be strongest at small spatial scales.2. In an early stage temperate tree diversity experiment, we monitored damage from leaf removing herbivores, specialist (gallers and leaf miners) herbivores, and two special… Show more
“…This supports former evidence suggesting that foliar fungal pathogens have the potential to maintain competitive differences between tree species (Spear & Mordecai, 2018) and can be regulated by the diversity of the surrounding tree community (Grossman et al, 2019).…”
This article has been accepted for publication and undergone full peer review but has not been through the copyediting, typesetting, pagination and proofreading process, which may lead to differences between this version and the Version of Record. Please cite this article as
“…This supports former evidence suggesting that foliar fungal pathogens have the potential to maintain competitive differences between tree species (Spear & Mordecai, 2018) and can be regulated by the diversity of the surrounding tree community (Grossman et al, 2019).…”
This article has been accepted for publication and undergone full peer review but has not been through the copyediting, typesetting, pagination and proofreading process, which may lead to differences between this version and the Version of Record. Please cite this article as
“…First, it may reflect increasing complementarity effects dependent on the dispersion of functional traits not correlated with shade tolerance dissimilarity (Paquette et al ). Second, higher phylogenetic dissimilarity may buffer trees against the negative effects of specialist pest and pathogen outbreaks (Parker et al ; Grossman et al ). Studies have suggested that outbreaks of pests such as spruce budworm have increased in intensity in our study region (Boucher et al ) and regions previously inaccessible to the pest due to cold temperatures will become more susceptible as the climate warms (Pureswaran et al ).…”
Section: Discussionmentioning
confidence: 99%
“…Furthermore, phylogenetic dissimilarity may affect tree growth through a reduction in susceptibility to species–specific pests, pathogens and/or predators. Originally developed to describe patterns of seedling recruitment (Janzen ; Connell ), this theory has been extended to mature plants in the form of the resource concentration hypothesis (Parker et al ; Grossman et al ). The theory stipulates that mature plant communities with high abundances of phylogenetically close host species are more susceptible to specialised pest and pathogen outbreak than those with higher phylogenetic dissimilarity.…”
Increases in niche complementarity have been hypothesised to reduce the intensity of interspecific competition within natural forests. In regions currently experiencing potentially enhanced growth under global environmental change, niche complementarity may become even more beneficial. However, few studies have provided direct evidence of this mechanism. Here, we use data from 180 permanent sample plots in Manitoba, Canada, with a full spatial mapping of all stems, to show that complementarity effects on average increased with neighbourhood competition intensity and temporally rising CO2, warming and water availability. Importantly, complementarity effects increased with both shade tolerance and phylogenetic dissimilarity between the focal tree and its neighbours. Our results provide further evidence that increasing stand functional and phylogenetic diversity can improve individual tree productivity, especially for individuals experiencing intense competition and may offer an avenue to maintain productivity under global environmental change.
“…Here, for reference, we include stand-replacing fire, a common disturbance type of stand-replacing disturbances in North America as an example. Previous studies have revealed that resource conditions are liable to be affected by stand-replacing fire disturbances [8,12,[33][34][35], which result in increased light, soil nutrients, pH, and soil temperatures, and a decrease in the organic layer depth [15]. Immediately after fire, adequate growth space and resource availability greatly favor the establishment of vascular plants, which are fast-growing, nutrient-demanding, and shade-intolerant [8].…”
Understorey vegetation comprises a major portion of plant diversity and contributes greatly to nutrient cycling and energy flow. This review examines the mechanisms involved in the response of understorey vegetation to stand development and the overstorey canopy following disturbances. The overall abundance and diversity of the understorey is enhanced with the availability and heterogeneity of light, soil nutrients, soil moisture, and substrates. Vascular plants are positively impacted by the availability and heterogeneity of light and soil nutrients, whereas non-vascular vegetation is more strongly influenced by colonization time, soil moisture, and substrates, and is decreased with a higher proportion of broadleaf overstorey. The availability of resources is a prominent driver toward the abundance and diversity of understorey vegetation, from the stand initiation to stem exclusion stage under a single-species dominated overstorey. However, resource heterogeneity dominates at the later stages of succession under a mixed overstorey. Climate and site conditions modify resource availability and heterogeneity in the understorey layer, but the extent of their influences requires more investigation. Forest management practices (clearcutting and partial harvesting) tend to increase light availability and heterogeneity, which facilitates the abundance and diversity of understorey vascular plants; however, these factors reduce the occurrence of non-vascular plants. Nevertheless, in the landscape context, anthropogenic disturbances homogenize environmental conditions and reduce beta-diversity, as well, the long-term effects of anthropogenic disturbances on understorey vegetation remain unclear, particularly compared with those in primary forests.
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