Abstract

Ectomycorrhizal fungi are an essential component of forest ecosystems, most of which can form edible and medical fruiting bodies. Although many studies have focused on the fructification of ectomycorrhizal fungi in phenology, the impact of environmental contamination, especially living garbage, on the formation of fruiting body is still unknown. A field investigation, combined with a high‐throughput sequencing method, was used to study the effect of living garbage pollution on the fructification and hypogeous community structure of ectomycorrhizal fungi symbiosing with cedar (Cedrus deodara (Roxb.) G. Don). The results showed that garbage significantly altered soil abiotic and biotic properties, increasing soil urease activity, decreasing the soil exchangeable metal content and phosphatase activity, and ultimately inhibiting the formation of fruiting bodies. The pollution of garbage also changed the community structure of hypogeous ectomycorrhizal fungi where ectomycorrhizal ascomycetes dominated. In unpolluted sites, the relative abundance of ectomycorrhizal ascomycetes and basidiomycetes were almost equal. Although no fruiting bodies were observed in that soil polluted by living garbage, the sequencing result showed that various ectomycorrhizal fungi were present underground, suggesting that these taxonomic fungi had the potential to cope with adverse conditions. This study not only provided a deeper understanding of the relationship between ectomycorrhizal fungal communities and prevailing environmental conditions, but provided a new pathway for the excavation and utilization of the resource of antistress ectomycorrhizal fungi.

Highlights

  • Ectomycorrhizal (ECM) fungi are one of the most important participants in nutrient cycling in terrestrial ecosystems, especially for nitrogen, phosphorus, and potassium (Behie & Bidochka, 2014; Cairney, 2011; Nasholm, Kielland, & Ganeteg, 2009; Szuba, 2015)

  • It is necessary to study the fructification and community structure of ECM fungi under different environmental conditions, which contributes to the understanding of the effect of environmental disruption on these two aspects

  • Many ECM fungi can be observed in the summer and autumn seasons beneath such cedar trees, few are seen near the campus avenues adjacent to living garbage dumps, mainly consist of plastics, waste paper and clothes, building wastes, few food residues, etc

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Summary

| MATERIALS AND METHODS

Three cedar trees with an accumulation of garbage in the immediate vicinity were randomly chosen as polluted sites (PS) on 11 September, 2015. The remainder soil samples were stored at 4°C for determination of enzyme activity, or at −80°C for ECM fungal DNA extraction. Sequencing libraries were generated using TruSeq® DNA PCR-­Free Sample Preparation Kit (Illumina, USA) following manufacturer’s recommendations and index codes were added. Rarefaction curves of all samples are shown, indicating that sequencing depth can reveal soil fungal community composition. ECM fungal community structures of different sites were completely dissimilar (Adonis p = .003, R2 = 0.376, number of permutations = 9999). The Mantel test indicated a highly significant correlation between environmental variables (exchangeable K+ and exchangeable Mg2+, and urease activity) and ECM fungal community (r = .33, p = .004; r = .40, p = .003; r = 0.25, p = .017, respectively)

Findings
| DISCUSSION
| CONCLUSION
Full Text
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