Abstract:Wildfire affects our planet's biogeochemistry both by burning biomass and by driving changes in ecological communities and landcover. Some plants and ecosystem types are threatened by increasing fire pressure while others respond positively to fire, growing in local and regional abundance when it occurs regularly. However, quantifying total ecosystem response to fire demands consideration of impacts not only on aboveground vegetation, but also on soil microbes like fungi, which influence decomposition and nutr… Show more
“…We also compared the relative abundance and species richness of saprotrophic, pathogenic, and mycorrhizal functional guilds among garlic mustard treatments and between sampling dates using FUNGuild (Nguyen et al, 2016) to assign functional guild to taxa. Assignments with “probable” or “highly probable” confidence scores were included, and in cases where taxa were assigned to more than one guild, mycorrhizal classification was given higher priority than pathogenic, which was given higher priority than saprotrophic guild (Smith et al, 2021).…”
The invasive forest plant garlic mustard (Alliaria petiolata) has been shown to alter soil microbial communities in the northeastern part of its invaded range in the United States, and this disruption of soil communities may contribute to its invasion success. However, garlic mustard allelochemistry can vary with invasion age, and it is not clear whether garlic mustard's impacts on soil microbes are consistent over its invaded range. Here, we compare the composition and diversity of soil fungal, bacterial, and archaeal communities among garlic mustard present, absent, and removed treatments in replicated blocks across five forests in the midwestern United States with relatively young garlic mustard invasions (approximately 17-26 years old, with consistent management). We collected samples in May and August, corresponding to garlic mustard active and senescent life history stages. While soil fungal and bacterial/ archaeal communities (based on ITS2 region and 16S rRNA gene DNA sequencing, respectively) differed significantly between different blocks/forests and over time, we found no significant effect of garlic mustard treatment on soil microbial community composition or the relative abundance of mycorrhizal, saprotrophic, or pathogenic fungal guilds. The lack of garlic mustard impacts on the soil microbial community in recently invaded central Illinois forests suggests that these well-documented impacts in the northeastern United States and in older invasions cannot necessarily be generalized across all environmental contexts.
“…We also compared the relative abundance and species richness of saprotrophic, pathogenic, and mycorrhizal functional guilds among garlic mustard treatments and between sampling dates using FUNGuild (Nguyen et al, 2016) to assign functional guild to taxa. Assignments with “probable” or “highly probable” confidence scores were included, and in cases where taxa were assigned to more than one guild, mycorrhizal classification was given higher priority than pathogenic, which was given higher priority than saprotrophic guild (Smith et al, 2021).…”
The invasive forest plant garlic mustard (Alliaria petiolata) has been shown to alter soil microbial communities in the northeastern part of its invaded range in the United States, and this disruption of soil communities may contribute to its invasion success. However, garlic mustard allelochemistry can vary with invasion age, and it is not clear whether garlic mustard's impacts on soil microbes are consistent over its invaded range. Here, we compare the composition and diversity of soil fungal, bacterial, and archaeal communities among garlic mustard present, absent, and removed treatments in replicated blocks across five forests in the midwestern United States with relatively young garlic mustard invasions (approximately 17-26 years old, with consistent management). We collected samples in May and August, corresponding to garlic mustard active and senescent life history stages. While soil fungal and bacterial/ archaeal communities (based on ITS2 region and 16S rRNA gene DNA sequencing, respectively) differed significantly between different blocks/forests and over time, we found no significant effect of garlic mustard treatment on soil microbial community composition or the relative abundance of mycorrhizal, saprotrophic, or pathogenic fungal guilds. The lack of garlic mustard impacts on the soil microbial community in recently invaded central Illinois forests suggests that these well-documented impacts in the northeastern United States and in older invasions cannot necessarily be generalized across all environmental contexts.
“…We do not observe that Douglas-firs facilitate oak colonization to the same extent, potentially due to stricter hostspecificity in Douglas-fir root fungal communities (Figure 4). Third, we observed significant but variable effects of fire on root fungal colonization (Figure 1), richness (Figure 2) and community structure (Figure 3), demonstrating that fire-driven shifts in soil fungal communities (Smith et al, 2021) translate to differences in root-associated fungal community assembly. In support of H3, we found negative effects of fire on fungal species richness with both Douglas-fir and oak when growing in Douglas-fir forest soil, and a negative effect of fire on root fungal colonization in oak seedlings in Douglas-fir forest soil.…”
Section: Df Forest Soilmentioning
confidence: 85%
“…We chose this distance because prior investigation of ectomycorrhizal fungi found that spatial autocorrelation was limited to approximately 3 m distance (Lilleskov et al, 2004). Moreover, a prior study in this system found that the minor influence of geography on soil fungal community composition relative to other predictors increased most rapidly among the shortest pairwise distances (Smith et al, 2021). This indicates that even small spatial distances between samples create differences in community composition that are large relative to the maximum potential impact of geography, minimizing the potential statistical challenge of spatial autocorrelation in this system.…”
1. Self-reinforcing differences in fire frequency help closed-canopy forests, which resist fire, and open woodlands, which naturally burn often, to co-occur stably at landscape scales. Forest tree seedlings, which could otherwise encroach and overgrow woodlands, are killed by regular fire, yet fire has other effects that may also influence these feedbacks. In particular, many forest trees require symbiotic ectomycorrhizal fungi in order to establish. By restructuring soil fungal communities, fire might affect the availability of symbionts or the potential for symbiont sharing between encroaching trees and woodland vegetation.2. To investigate this possibility, we performed a soil bioassay experiment using inoculum from burned and unburned oak woodlands and Douglas-fir forests.We examined how fire, ecosystem type, and neighboring heterospecific seedlings affect fungal root community assembly of Douglas-firs and oaks. We asked whether heterospecific seedlings facilitated fungal colonization of seedling roots in non-native soil, and if so, whether fire influenced this interaction.3. External fungal colonization of oak roots was more influenced by fire and ecosystem type than by the presence of a Douglas-fir, and oaks increased the likelihood that Douglas-fir roots would be colonized by fungi in oak woodland soil. Yet, fire increased colonization of Douglas-fir in oak soil, diminishing the otherwise crucial role played by oak facilitation. Fire also strengthened the positive effect of Douglas-firs on oak root-associated fungal diversity in Douglas-fir forest soil.4. Prior work shows that fire supports woodland ecosystems by stemming recruitment of encroaching seedlings. Here, we find evidence that it may contrastingly reduce fungal limitation of invasive seedling growth and establishment, otherwise relieved only by facilitation. Future work can investigate how these opposing effects might contribute to the net impact of changes in fire regime on landcover stability.
“…We also compared the relative abundance and species richness of saprotrophic, pathogenic, and mycorrhizal functional guilds among garlic mustard treatments and between sampling dates using FUNGuild (Nguyen et al 2016) to assign functional guild to taxa. Assignments with “probable” or “highly probable” confidence scores were included and in cases where taxa were assigned to more than one guild, mycorrhizal classification was given higher priority than pathogenic, which was given higher priority than saprotrophic (Smith et al 2021).…”
Garlic mustard (Alliaria petiolata) has long been known to degrade mycorrhizal mutualisms in soils it invades and may also promote the abundance of microbial pathogens harmful to native plants or alter saprotrophic communities to disrupt nutrient cycling. Phenology of other invasive species, like Lepidium latifolium and Lonicera maackii, plays a role in their interactions with soil microbial communities, and so we may expect garlic mustard phenology to influence its effects on native soil microbiomes as well. Here, we investigate differences in fungal, bacterial, and archaeal community structure, as well as the abundance of key functional groups, between garlic mustard present, absent, and removed treatments in central-Illinois forest soils across different stages of the garlic mustard life cycle. Across its phenology, garlic mustard present soils had different overall fungal community structure and greater abundance of pathotrophic fungi than soils where garlic mustard was absent or removed. However, abundance of ectomycorrhizal and saprotrophic fungi as well as bacterial and archaeal community structure were similar between treatments and did not interact with garlic mustard phenology. The most abundant overall fungal taxon was a plant pathogen, Entorrhiza aschersoniana, that was greatest in garlic mustard present soils, particularly while the plants were flowering. These results support the hypothesis that invasive plants form active relationships with microbial pathogens that could contribute to their overall success in invading ecosystems.
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