4.7 Article

Arbuscular mycorrhizal trees cause a higher carbon to nitrogen ratio of soil organic matter decomposition via rhizosphere priming than ectomycorrhizal trees

期刊

SOIL BIOLOGY & BIOCHEMISTRY
卷 157, 期 -, 页码 -

出版社

PERGAMON-ELSEVIER SCIENCE LTD
DOI: 10.1016/j.soilbio.2021.108246

关键词

Mycorrhizal fungi; Enzyme stoichiometry; Soil carbon mineralization; Gross nitrogen mineralization; Rhizosphere priming; Tree seedlings

资金

  1. National Key Research and Development Program of China [2016YFA0600801]
  2. National Natural Science Foundation of China [31470625, 41630755, 31971635]
  3. U.S. Department of Energy Office of Biological and Environmental Research, Terrestrial Ecosystem Science Program [DESC0016188]

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Tree roots and their associated microbes can significantly influence soil organic matter decomposition, with AM-associated trees inducing greater soil C decomposition than ECM-associated trees. AM-associated trees have higher C-degrading enzyme activities and lower N-degrading enzyme activities, resulting in a higher C:N ratio of SOM decomposition compared to ECM-associated trees.
Tree roots and their associated microbes can significantly influence soil organic matter (SOM) decomposition, i. e., the rhizosphere priming effect. This effect is expected to be greater in trees associated with arbuscular mycorrhizal (AM) fungi, which produce higher extracellular enzymes especially surrounding hyphae, than in trees associated with ectomycorrhizal (ECM) fungi. Here, we selected five tree species associated with AM (Juglans mandshurica Maxim. and Cunninghamia lanceolata (Lamb.) Hook.) or ECM (Picea koraiensis Nakai, Quercus mongolica Fischer ex Turcz. and Larix kaempferi (Lamb.) Carriere). We grew tree seedlings inside of cores lined with different mesh sizes to investigate how roots, hyphae and exudates influence soil carbon (C) and nitrogen (N) mineralization via the rhizosphere priming effect, using a(13)C natural abundance approach and a(15)N pool dilution method, concurrently. We found that tree seedlings significantly accelerated soil C decomposition by on average 78%, i.e., positive priming, compared to unplanted control pots. AM-associated trees induced 2.1 times greater soil C decomposition than ECM-associated trees across all mesh sizes. In contrast, gross N mineralization did not differ between tree-mycorrhizal associations. Compared to ECM counterparts, AM-associated trees had higher C- and lower N-degrading enzyme activities. Consequently, AM-associated trees induced a significantly higher C:N ratio of SOM decomposition than their ECM counterparts, which could be associated with the differences in soil enzyme activities for C and N degradation. Further, for both AM- and ECM-associated trees, we found no significant influences of mesh size on soil C decomposition, suggesting that the rhizosphere priming effect of mycorrhizal symbiosis was predominantly driven by root exudates. We conclude that SOM decomposition caused by AM-associated trees may have a higher C:N ratio than that by ECM-associated trees mainly due to differences in microbial enzyme investment. Our findings imply that tree-mycorrhizal associations are capable of modulating soil biogeochemical cycling via the rhizosphere priming effect.

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