Abstract
The mycorrhizal symbiosis between fungi and plants is among the oldest, ubiquitous and most important interactions in terrestrial life on Earth. Carbon (C) transfer across a common mycorrhizal network (CMN) was demonstrated over half a century ago in the lab ( Reid & Woods, 1969), and later in the field ( Simard et al., 1997a). Recent years have seen ample progress in this research direction, including evidence for ecological significance of carbon transfer ( Klein et al., 2016). Furthermore, specific cases where the architecture of mycorrhizal networks have been mapped ( Beiler et al., 2015) and CMN-C transfer from mature trees to seedlings has been demonstrated ( Orrego, 2018) have suggested that trees in forests are more connected than once thought ( Simard, 2021). In a recent Perspective, Karst et al. (2023) offered a valuable critical review warning of over-interpretation and positive citation bias in CMN research. It concluded that while there is evidence for C movement among plants, the importance of CMNs remains unclear, as noted by others too ( Henriksson et al., 2023). Here we argue that while some of these claims are justified, factual evidence about belowground C transfer across CMNs is solid and accumulating.
Keywords: common mycorrhizal network, belowground carbon transfer, root carbon uptake, mycorrhizal exchange, isotopic carbon labeling, dual mycorrhization
Plain language summary
Mycorrhizas are fungal associations between plant roots and beneficial fungi (mushrooms). In forests, some of these belowground associations can include more than one tree, creating a common mycorrhizal network (CMN). It has been shown in multiple studies that CMNs can serve as transport pathways of carbon among different trees. Recently, Karst et al. (2023) offered a valuable critical review questioning the importance of CMNs, as noted by others too ( Henriksson et al., 2023). Here we argue that factual evidence about belowground C transfer across CMNs is solid and accumulating and discuss current questions in CMN research.
Recently, Cahanovitc et al. (2022) showed unequivocally, using DNA-stable isotope probing, 13C in the DNA of specific mycorrhizal species colonizing roots of both donor and recipient saplings, growing in forest soil under natural conditions. In addition, the label was found not on roots only, but also in stems, as previously seen in mature trees in the forest ( Klein et al., 2016). Remaining questions are (1) Why is CMN-C transfer so elusive? (2) How important are alternative transfer pathways? (3) What is the significance for trees? (4) How can we explain the counterintuitive C transfer from fungus to the recipient tree? And finally, (5) What is the benefit to the fungus? The next few paragraphs offer answers to these key questions.
(1) Why is CMN-C transfer so elusive? Multiple labeling experiments detect CMN-C transfer, while others do not ( Karst et al., 2023). Often, this is because labeling intensity is too low to detect an otherwise small C flow due to high labeling material costs. Regardless, chances are meager to collect the specific root with specific mycorrhizal fungi at the exact time of C transfer due to the spatial and dynamic complexity of the CMN ( Read et al., 1985). The mycorrhizal community of mature trees differs on every root, even among root tips on the same root branchlet ( Rog et al., 2020; Rog et al., 2022). Furthermore, trees allocate different amounts of C to varying roots according to soil niche, microbial community, and other root trait parameters. Trees of various species occupy different soil niches; mycorrhizal species are also located in different depths ( Toju et al., 2016). The ecological significance of C transfer among different tree species can be masked by the complexity of host tree roots and CMNs.
(2) How important are alternative transfer pathways? These include respiration, exudation, turnover, mass flow, assimilation, and redistribution by soil biota ( Henriksson et al., 2023). These pathways probably can never be completely ruled out. However, C flow through fungal mycelium is much more efficient than through bulk soil because it bypasses soil microbial assimilation and transformation. Diffusional mass flow in unsaturated soil is in the magnitude of m month -1, and its temporal dynamics rarely match those of the observed label transfer ( Avital et al., 2022). In addition, exudates rarely travel more than a few mm in soil without active transport ( Kuzyakov et al., 2003). It is obviously possible that one fungus’ hyphae exudate C compounds that are consequently acquired by neighboring fungal hyphae (not belonging to the same mycelium; Karst et al., 2023). Still, a forest study showed lack of label transfer to plants hosting other mycorrhizal types and lack of label transfer to saprotrophic fungi ( Klein et al., 2016). Simard et al. (1997a) also found a fraction of C label transferred to tree seedlings not involved in a CMN compared to those that were. These studies support the notion that C is moving through hyphal networks from one plant to another.
(3) What is the significance for trees? A traditional view often measures benefit to trees based on growth enhancement, such as stem height, diameter, or biomass. However, it should be noted that C transfer is typically small compared to autotrophic C assimilation, making it less likely to have a direct impact on the recipient’s growth. Hence, the significance of the CMN-C transfer is probably more nuanced, e.g., in providing C for osmoregulation ( Sapes et al., 2021) or defense metabolite transfer ( Song et al., 2015). It is also important to mention that many plants (including trees) are nutrient-limited and not C-limited ( Körner, 2015; Kiers & van der Heijden, 2006). There are probably no strong evolutionary selection pressures to prevent C loss if C is a luxury good through most of the lifespan of a tree and if delivering this C to the CMN is also linked to benefits (e.g. nutrients provided by the CMN). Likewise, trees that may benefit from it, are limited in C source (e.g., due to deep shade; Simard et al., 1997b) or are either disproportionally short in C sources compared to adjacent bigger and older trees ( Simard et al., 1997b).
(4) How can we explain the counterintuitive C transfer from fungus to the recipient tree? Is it physiologically feasible? Levels of hexose are consistently higher in the host roots compared to the fungus, making it difficult for hexose to move against this gradient ( Henriksson et al., 2023). This holds true in most situations. However, there is an exception when the recipient tree is subjected to heavy shading. In such cases, the roots of the recipient tree may experience C depletion, as suggested by Sapes et al. (2021), thereby reversing the hexose "gradient" from fungi to roots. Moreover, C has been shown to transfer to host trees along with N, most likely in amino acids ( Teste et al., 2009).
(5) What is the benefit to the fungus? C flow from the donor tree is clear, given that the fungus is inherently heterotrophic, thus C-supply dependent. C flow also exists from fungus to plant: myco-heterotrophic plants that lack chlorophyll obtain C from other plants by parasiting on CMNs throughout their lifespan ( Leake, 2005). Moreover, approximately 25,000 orchid species live in symbiosis with mycorrhizal fungi ( van der Heijden et al., 2008). Young orchid seeds are extremely small (0.3–14 µg), lack chlorophyll and it is thought that the germinating seeds (protocorms) of almost all orchids obtain C and nutrients from their mycorrhizal symbionts, sometimes for years, before a green and autotrophic plant emerge ( Cameron et al., 2008). These are clear examples that C transfer from CMN to plants does occur. Yet what is the adaptive advantage of C flow from fungus to an autotrophic recipient tree? Mycorrhizal symbiosis is traditionally viewed as a belowground, cross-kingdom, exchange of carbohydrates (plant→fungus) for nutrients (fungus→plant). However, contemporary research offers a more complex view, whereby fatty acids and lipids are transferred between mycorrhizal fungi and plant hosts ( Jiang et al., 2017). In addition, C transfer in the form of amino acids ( Simard et al., 2012) inescapably involves N transfer, going both ways. Thus, a fungus→plant C movement is not unlikely when C is tied to nutrients (e.g. amino acids) or when trees or plants acquire C from degenerating hyphae in the Hartig Net (as in AMF arbuscules).
The above point (5) aligns with the notion that competition for light, water, and nutrients is still a major interaction in forests ( Henriksson et al., 2023; Klein et al., 2016). Specific mycorrhizal fungi transfer C among trees, including from canopy trees to seedlings, or from sunlit saplings to shaded saplings of the same, or different (non-kin), species. This facilitative behavior has been demonstrated by Teste et al. (2009) and Bingham & Simard (2012) in temperate forests but requires further testing in different biomes. C transfer takes place between different, unrelated tree species sharing mycorrhizal species ( Avital et al., 2022; Rog et al., 2020). This includes C transfer between an EM-host to an AM-host with dual mycorrhization status ( Cupressus sempervirens; Avital et al., 2022). Interestingly, some of the mycorrhizal species involved in C transfer among temperate trees (e.g. Russula chloroides; Rog et al., 2020) and among Mediterranean trees (e.g. Tomentella ellisii; Cahanovitc et al., 2022) were also identified in myco-heterotrophic plants ( Girlanda et al., 2006; Julou et al., 2005).
Finally, an evolutionary advantage should exist for fungi to maintain diversity of tree hosts and hence C sources ( Tedersoo et al., 2020). For example, in a mixed Mediterranean forest, tree species diverge in their phenologies and functions ( Rog et al., 2021), and multi-host EMF and AMF form the vast majority of mycorrhizal species ( Rog et al., 2022). Indeed, mycorrhizal fungi are not merely conduits for tree-tree resource sharing, but rather complex organisms having their own strategies ( Henriksson et al., 2023). Without a mechanism for tree-directed C transfer across CMNs, it is most probably driven by the fungi, rather than by the trees. There is a need for more experimental studies to visualize that a single mycorrhizal mycelium interconnects different trees and to assess when and how much C is moving from one tree to another. However, there is sufficient evidence that trees in forests are connected by a CMN and transmitting C among themselves, and this can lead to new management practices that tend to the whole forest rather than individual trees, thus improving the ability of forests to cope with stress. The next few years might shed new light on how CMNs and C transfer may affect forest resilience, as the field is rapidly evolving.
Ethics and consent
Ethical approval and consent were not required.
Acknowledgements
The authors thank Suzanne Simard (UBC, Canada) for helpful comments made on an earlier version of this paper.
Funding Statement
TK has received funding from the European Research Council (ERC) under the European Union’s Horizon 2020 research and innovation programme (Grant agreement No. 849740).
The funders had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.
[version 1; peer review: 1 approved, 2 approved with reservations]
Data availability
No data are associated with this article.
References
- Avital S, Rog I, Livne‐Luzon S, et al. : Asymmetric belowground carbon transfer in a diverse tree community. Mol Ecol. 2022;31(12):3481–3495. 10.1111/mec.16477 [DOI] [PMC free article] [PubMed] [Google Scholar]
- Beiler KJ, Simard SW, Durall DM: Topology of tree–mycorrhizal fungus interaction networks in xeric and mesic Douglas-fir forests. J Ecol. 2015;103(3):616–628. 10.1111/1365-2745.12387 [DOI] [Google Scholar]
- Bingham MA, Simard S: Ectomycorrhizal networks of Pseudotsuga menziesii var. glauca trees facilitate establishment of conspecific seedlings under drought. Ecosystems. 2012;15:188–199. 10.1007/s10021-011-9502-2 [DOI] [Google Scholar]
- Cahanovitc R, Livne-Luzon S, Angel R, et al. : Ectomycorrhizal fungi mediate belowground carbon transfer between pines and oaks. ISME J. 2022;16(5):1420–1429. 10.1038/s41396-022-01193-z [DOI] [PMC free article] [PubMed] [Google Scholar]
- Cameron DD, Johnson I, Read DJ, et al. : Giving and receiving: measuring the carbon cost of mycorrhizas in the green orchid, Goodyera repens. New Phytol. 2008;180(1):176–184. 10.1111/j.1469-8137.2008.02533.x [DOI] [PubMed] [Google Scholar]
- Girlanda M, Selosse MA, Cafasso D, et al. : Inefficient photosynthesis in the Mediterranean orchid Limodorum abortivum is mirrored by specific association to ectomycorrhizal Russulaceae. Mol Ecol. 2006;15(2):491–504. 10.1111/j.1365-294X.2005.02770.x [DOI] [PubMed] [Google Scholar]
- Henriksson N, Marshall J, Högberg MN, et al. : Re‐examining the evidence for the mother tree hypothesis – resource sharing among trees via ectomycorrhizal networks. New Phytol. 2023;239(1):19–28. 10.1111/nph.18935 [DOI] [PubMed] [Google Scholar]
- Jiang Y, Wang W, Xie Q, et al. : Plants transfer lipids to sustain colonization by mutualistic mycorrhizal and parasitic fungi. Science. 2017;356(6343):1172–1175. 10.1126/science.aam9970 [DOI] [PubMed] [Google Scholar]
- Julou T, Burghardt B, Gebauer G, et al. : Mixotrophy in orchids: insights from a comparative study of green individuals and nonphotosynthetic individuals of Cephalanthera damasonium. New Phytol. 2005;166(2):639–653. 10.1111/j.1469-8137.2005.01364.x [DOI] [PubMed] [Google Scholar]
- Karst J, Jones MD, Hoeksema JD: Positive citation bias and overinterpreted results lead to misinformation on common mycorrhizal networks in forests. Nat Ecol Evol. 2023;7(4):501–511. 10.1038/s41559-023-01986-1 [DOI] [PubMed] [Google Scholar]
- Kiers ET, van der Heijden MGA: Mutualistic stability in the arbuscular mycorrhizal symbiosis: exploring hypotheses of evolutionary cooperation. Ecology. 2006;87(7):1627–1636. 10.1890/0012-9658(2006)87[1627:msitam]2.0.co;2 [DOI] [PubMed] [Google Scholar]
- Klein T, Siegwolf RT, Körner C: Belowground carbon trade among tall trees in a temperate forest. Science. 2016;352(6283):342–344. 10.1126/science.aad6188 [DOI] [PubMed] [Google Scholar]
- Kuzyakov Y, Raskatov A, Kaupenjohann M: Turnover and distribution of root exudates of Zea mays. Plant and Soil. 2003;254:317–327. 10.1023/A:1025515708093 [DOI] [Google Scholar]
- Körner C: Paradigm shift in plant growth control. Curr Opin Plant Biol. 2015;25:107–114. 10.1016/j.pbi.2015.05.003 [DOI] [PubMed] [Google Scholar]
- Leake JR: Plants parasitic on fungi: unearthing the fungi in myco-heterotrophs and debunking the ‘saprophytic’plant myth. Mycologist. 2005;19(3):113–122. 10.1017/S0269-915X(05)00304-6 [DOI] [Google Scholar]
- Orrego G: Western hemlock regeneration on coarse woody debris is facilitated by linkage into a mycorrhizal network in an old-growth forest. (Doctoral dissertation, University of British Columbia),2018. Reference Source [Google Scholar]
- Read D, Francis R, Finlay RD: Mycorrhizal mycelia and nutrient cycling in plant communities. In: Fitter, A.H. (Ed.), Ecological Interactions in Soil. Blackwell Sci. Publs, Oxford,1985;131–217. [Google Scholar]
- Reid CPP, Woods FW: Translocation of C^(14)‐Labeled Compounds in Mycorrhizae and It Implications in Interplant Nutrient Cycling. Ecology. 1969;50(2):179–187. 10.1101/2022.08.01.502298v1 [DOI] [Google Scholar]
- Rog I, Lewin-Epstein O, Livne-Luzon S, et al. : Prosperity of the commons: Generalist mycorrhizal species dominate a mixed forest and may promote forest diversity by mediating resource sharing among trees. bioRxiv. 2022; 2022-08. 10.1101/2022.08.01.502298 [DOI] [Google Scholar]
- Rog I, Rosenstock NP, Körner C, et al. : Share the wealth: Trees with greater ectomycorrhizal species overlap share more carbon. Mol Ecol. 2020;29(13):2321–2333. 10.1111/mec.15351 [DOI] [PMC free article] [PubMed] [Google Scholar]
- Rog I, Tague C, Jakoby G, et al. : Interspecific soil water partitioning as a driver of increased productivity in a diverse mixed Mediterranean forest. JGR: Biogeosciences. 2021;126(9): e2021JG006382. 10.1029/2021JG006382 [DOI] [Google Scholar]
- Sapes G, Demaree P, Lekberg Y, et al. : Plant carbohydrate depletion impairs water relations and spreads via ectomycorrhizal networks. New Phytol. 2021;229(6):3172–3183. 10.1111/nph.17134 [DOI] [PubMed] [Google Scholar]
- Simard S: Finding the Mother Tree: Discovering the Wisdom of the Forest. Knopf Doubleday Publishing Group, New York, USA,2021. Reference Source [Google Scholar]
- Simard SW, Beiler KJ, Bingham MA, et al. : Mycorrhizal networks: mechanisms, ecology and modelling. Fungal Biol Rev. 2012;26(1):39–60. 10.1016/j.fbr.2012.01.001 [DOI] [Google Scholar]
- Simard SW, Jones MD, Durall DM, et al. : Reciprocal transfer of carbon isotopes between ectomycorrhizal Betula papyrifera and Pseudotsuga menziesii. New Phytol. 1997a;137(3):529–542. 10.1046/j.1469-8137.1997.00834.x [DOI] [PubMed] [Google Scholar]
- Simard SW, Perry DA, Jones MD, et al. : Net transfer of carbon between ectomycorrhizal tree species in the field. Nature. 1997b;388(6642):579–582. 10.1038/41557 [DOI] [Google Scholar]
- Song YY, Simard SW, Carroll A, et al. : Defoliation of interior Douglas-fir elicits carbon transfer and stress signalling to ponderosa pine neighbors through ectomycorrhizal networks. Sci Rep. 2015;5(1): 8495. 10.1038/srep08495 [DOI] [PMC free article] [PubMed] [Google Scholar]
- Tedersoo L, Bahram M, Zobel M: How mycorrhizal associations drive plant population and community biology. Science. 2020;367(6480): eaba1223. 10.1126/science.aba1223 [DOI] [PubMed] [Google Scholar]
- Teste FP, Simard SW, Durall DM, et al. : Access to mycorrhizal networks and roots of trees: importance for seedling survival and resource transfer. Ecology. 2009;90(10):2808–2822. 10.1890/08-1884.1 [DOI] [PubMed] [Google Scholar]
- Toju H, Kishida O, Katayama N, et al. : Networks depicting the fine-scale co-occurrences of fungi in soil horizons. PLoS One. 2016;11(11): e0165987. 10.1371/journal.pone.0165987 [DOI] [PMC free article] [PubMed] [Google Scholar]
- Van Der Heijden MG, Bardgett RD, Van Straalen NM: The unseen majority: soil microbes as drivers of plant diversity and productivity in terrestrial ecosystems. Ecol Lett. 2008;11(3):296–310. 10.1111/j.1461-0248.2007.01139.x [DOI] [PubMed] [Google Scholar]
