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26 results for “Ectomycorrhizal fungal community”
Figure 4 from: Meidl P, Furneaux B, Tchan KI, Kluting K, Ryberg M, Guissou M-L, Soro B, Traoré A, Konomou G, Yorou NS, Rosling A (2021) Soil fungal communities of ectomycorrhizal dominated woodlands across West Africa. MycoKeys 81: 45-68. https://doi.org/10.3897/mycokeys.81.66249
Figure 4 NMDS ordination of fungal communities based on Bray-Curtis dissimilarity of species hypothesis-based community composition, grouped into woodland (W) and gallery forests (GF) samples, for All fungi, axis 1–2 (A) and axis 2–3 (B), and for ECM fungi, axis 1–2 (C) and axis 3–4 (D). Stress value = 0.1902 for all fungi and 0.1723 for ECM fungi. Ellipses represent 95% confidence intervals around the mean of each vegetation type.
Figure 5 from: Meidl P, Furneaux B, Tchan KI, Kluting K, Ryberg M, Guissou M-L, Soro B, Traoré A, Konomou G, Yorou NS, Rosling A (2021) Soil fungal communities of ectomycorrhizal dominated woodlands across West Africa. MycoKeys 81: 45-68. https://doi.org/10.3897/mycokeys.81.66249
Figure 5 Fungal guild assignment of the soil fungal community in gallery forest and woodlands. Abundance measured as fraction of reads (A) and richness measured as fraction of species hypotheses (SH) (B) Guilds representing less than 2% of both abundance and richness are grouped together in "other".
Figure 2 from: Meidl P, Furneaux B, Tchan KI, Kluting K, Ryberg M, Guissou M-L, Soro B, Traoré A, Konomou G, Yorou NS, Rosling A (2021) Soil fungal communities of ectomycorrhizal dominated woodlands across West Africa. MycoKeys 81: 45-68. https://doi.org/10.3897/mycokeys.81.66249
Figure 2 NMDS ordination of tree communities based on Bray-Curtis dissimilarities between sites, based on total basal areas of each ECM trees species separately and all non-ECM trees combined. The nine sites were classified into two distinct woodland types, woodlands in red and gallery forests in blue. Site abbreviations: Bissandougou Forest Reserve (BISS-W), Moussaya Forest Reserve (MOUS-W), Kota Waterfall (KOTA-G and KOTA-W), Kouadianikro Forest Reserve (KDNK-W), Kou Forest Reserve (KOUF-G), Niangoloko Forest Reserve (NIAN-W) and Farako Forest Reserve (FA01-W and FA15-W). ECM tree species abbreviations: Afzelia africana (Aa), Ac: Anthonotha crassifolia (Ac), Bg: Berlinia grandiflora (Bg), Id: Isoberlinia doka (Id), I. tomentosa (It), Monotes kerstingii (Mk), Uapacaguineensis (Ug) and Uapaca togoensis (Ut).
Figure 1 from: Meidl P, Furneaux B, Tchan KI, Kluting K, Ryberg M, Guissou M-L, Soro B, Traoré A, Konomou G, Yorou NS, Rosling A (2021) Soil fungal communities of ectomycorrhizal dominated woodlands across West Africa. MycoKeys 81: 45-68. https://doi.org/10.3897/mycokeys.81.66249
Figure 1 Sampling sites of the West African Centre for Tropical Mycology's 2018 National Geographic Explorer Grant expedition. Shapes and colors separate the different woodland types with blue circles for gallery forests and red triangles for woodlands. With site names (abbreviations): Bissandougou (BISS-W), Moussaya (MOUS-W), Kota (KOTA-G and KOTA-W), Kouadianikro (KDNK-W), Kou (KOUF-G), Niangoloko (NIAN-W) and Farako (FA01-W and FA15-W). The dotted line represents the route taken on the sampling trip, beginning on the coast of Benin and concluding in Ivory Coast. Ecoregions are from White (1983), digitized in Olson et al. (2001).
Data from: Changes in ectomycorrhizal fungal community composition and declining diversity along a 2-million-year soil chronosequence
Ectomycorrhizal (ECM) fungal communities covary with host plant communities along soil fertility gradients, yet it is unclear whether this reflects changes in host composition, fungal edaphic specialization or priority effects during fungal community establishment. We grew two co-occurring ECM plant species (to control for host identity) in soils collected along a 2-million-year chronosequence representing a strong soil fertility gradient and used soil manipulations to disentangle the effects of edaphic properties from those due to fungal inoculum. Ectomycorrhizal fungal community composition changed and richness declined with increasing soil age; these changes were linked to pedogenesis-driven shifts in edaphic properties, particularly pH and resin-exchangeable and organic phosphorus. However, when differences in inoculum potential or soil abiotic properties among soil ages were removed while host identity was held constant, differences in ECM fungal communities and richness among chronosequence stages disappeared. Our results show that ECM fungal communities strongly vary during long-term ecosystem development, even within the same hosts. However, these changes could not be attributed to short-term fungal edaphic specialization or differences in fungal inoculum (i.e. density and composition) alone. Rather, they must reflect longer-term ecosystem-level feedback between soil, vegetation and ECM fungi during pedogenesis.
Data from: Changes in ectomycorrhizal fungal community composition and declining diversity along a 2-million-year soil chronosequence
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