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. 2023 Oct 3;3:168. [Version 1] doi: 10.12688/openreseurope.16594.1

Belowground carbon transfer across mycorrhizal networks among trees: Facts, not fantasy

Tamir Klein 1,a, Ido Rog 1,2, Stav Livne-Luzon 1, Marcel GA van der Heijden 2, Christian Körner 3
PMCID: PMC10751480  PMID: 38152158

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

  1. 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]
  2. 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]
  3. 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]
  4. 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]
  5. 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]
  6. 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]
  7. 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]
  8. 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]
  9. 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]
  10. 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]
  11. 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]
  12. 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]
  13. 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]
  14. 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]
  15. 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]
  16. 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]
  17. 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]
  18. 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]
  19. 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]
  20. 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]
  21. 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]
  22. 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]
  23. Simard S: Finding the Mother Tree: Discovering the Wisdom of the Forest. Knopf Doubleday Publishing Group, New York, USA,2021. Reference Source [Google Scholar]
  24. 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]
  25. 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]
  26. 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]
  27. 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]
  28. 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]
  29. 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]
  30. 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]
  31. 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]
Open Res Eur. 2023 Dec 26. doi: 10.21956/openreseurope.17913.r35982

Reviewer response for version 1

Marc-Andre Selosse 1

A very good, well-written and timely viewpoint, with many interesting ideas and appropriated references, bravo. It deserves urgent publication but I have a couple of comments below on missing issues. As COI, I have to cite some of my own work on mycoheterotrophic and mixotrophic plants (see my comments on this issue below*). Waiving anonymity, Marc-André Selosse

On question 1, one may mention the temporal issue (the C flux may happen, or not, or be reversed depending on time), as nicely illustrated by Lerat S, Gauci R, Catford JG, Vierheilig H, Piché Y, Lapointe L. 2002. 14C transfer between the spring ephemeral Erythronium americanum and sugar maple saplings via arbuscular mycorrhizal fungi in natural stands. Oecologia 132: 181–187. In this paper, the plant is an understory one but the author may not forget to mention the understory which may have strong need and may be a sink for tree C.

On question 2, C flow through fungal mycelium is also much more efficient than through bulk soil because it is directional, and thus avoids the dilution that happens in any isotropic mechanism.

On question 3, one may mention unequal reward that may be even more relevant: different plants associated to a same fungus they support may not (i) give same C amount and (ii) get the same amount of minerals, so that one plant may indirectly subsidize the mineral acquisition of another. It is an economy of C for the ‘winning plant’ which too overlooked while it is C-relevant! See (although they do not use trees) Florian Walder, Helge Niemann, Mathimaran Natarajan, Moritz F. Lehmann, Thomas Boller, Andres Wiemken, Mycorrhizal Networks: Common Goods of Plants Shared under Unequal Terms of Trade, Plant Physiology, Vol 159, 2, June 2012, Pages 789–797, https://doi.org/10.1104/pp.112.195727

On question 4 (see my comments on this issue below*), one may mention mycoheterotrophic and mixotrophic plants, where evidences point toward amino-acids as C source (Lallemand et al., 2019. In situ transcriptomic and metabolomic approach to the transition to the loss of photosynthesis in plants exploiting fungi. The Plant Journal 98: 826-841; Fochi et al., 2017. Fungal and plant gene expression in the Tulasnella calospora–Serapias vomeracea symbiosis provides clues about nitrogen pathways in orchid mycorrhizas. New Phytol 213, 365–379) and possibly trehalose (Li et al., 2022. Genomes of leafy and leafless Platanthera orchids illuminate the evolution of mycoheterotrophy. Nat Plants 8, 373–388).

On question 5, this is 28 000 orchids estimated by now and a more specific, accurate ref here would be Selosse et al., 2022 (The Waiting Room Hypothesis revisited: Were orchid mycorrhizal fungi recruited among root endophytes? Annals of Botany 129: 259–270). For the heterotrophic development (you may introduce here the word mycoheterotrophic), a review by Dearnaley et al., 2016. Structure and development of orchid mycorrhizas, in F. Martin (ed.) Molecular mycorrhizal symbiosis, p. 63-86. Wiley-Blackwell, Hoboken, New Jersey. ‘These are clear examples that C transfer from CMN to plants does occur’: no, it is most of the time not sure that the C extracted from fungi by protocorm is gained from surrounding plants (rhizoctonias have saprobic capacities). Yet, this is the case in mycoheterotrophic and mixotrophic seedlings (orchids and other), which are linked to ecto- or arbuscular- mycorrhizal fungi - in which case C transfer also occurs in adult plants (V. Merckx (ed.) 2013. Mycoheterotrophy: the biology of plants living on fungi, p. 297-342 (chap. 8). Springer, Berlin Heidelberg). I would avoid the issue of germination in orchids (which are not the sole to display mycoheterotrophic germination, by the way) but I would detail more mycoheterotrophic and mixotrophic (forest) plants, see my comments on this issue below*. Finally, on question 5, we already, with S. Simard and others, pointed the fungus-centered viewpoint that is often overlooked in a 2005 review (Mycorrhizal networks: les liaisons dangereuses. Trends in Ecology and Evolution 11 : 621-628).

*Finally, even if these are not trees, I would mention mycoheterotrophic and mixotrophic (= partially mycoheterotrophic) plants as they provide definite evidence of C transfer. By the way, the Limodorum we analyzed with M. Girlanda is not mixotrophic, but demonstrated partly photosynthetic – so, mixotrophic. Mycoheterotrophy and mixotrophy are currently too fast and superficially reported. One main problem (eg. in question 32) is the net contribution of C transfer to the receivers’ C budget. In mycoheterotrophs, this is 100%. In mixotrophs, this can be estimated from 13C content when the network is ectomycorrhizal, and rages from 0 to nearly 100% (see review in Selosse & Roy, 2009. Green plants eating fungi: facts and questions about mixotrophy. Shading has impact by increasing fungal exploitation (Matsuda et al., 2012. Seasonal and environmental changes of mycorrhizal associations and heterotrophy levels in mixotrophic Pyrola japonica (Ericaceae) growing under different light environments. American Journal of Botany 99: 1177-1188). Trends in Plant Sciences 14: 64-70); more over some achlorophyllous variant sometime survive in natura for mixotrophic species, in which 100% of C is of fungal origin (see Selosse & Roy, 2009, and Lallemand et al., 2019 already cited above).

Where applicable, are recommendations and next steps explained clearly for others to follow? (Please consider whether others in the research community would be able to implement guidelines or recommendations and/or constructively engage in the debate)

Not applicable

Does the article adequately reference differing views and opinions?

Partly

Are all factual statements correct, and are statements and arguments made adequately supported by citations?

Yes

Is the rationale for the Open Letter provided in sufficient detail? (Please consider whether existing challenges in the field are outlined clearly and whether the purpose of the letter is explained)

Yes

Is the Open Letter written in accessible language? (Please consider whether all subject-specific terms, concepts and abbreviations are explained)

Yes

Reviewer Expertise:

Symbiosis, mycology, mycorrhizas and their networks

I confirm that I have read this submission and believe that I have an appropriate level of expertise to confirm that it is of an acceptable scientific standard, however I have significant reservations, as outlined above.

References

  • 1. : Mycorrhizal networks: common goods of plants shared under unequal terms of trade. Plant Physiol .2012;159(2) : 10.1104/pp.112.195727 789-97 10.1104/pp.112.195727 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 2. : In situ transcriptomic and metabolomic study of the loss of photosynthesis in the leaves of mixotrophic plants exploiting fungi. Plant J .2019;98(5) : 10.1111/tpj.14276 826-841 10.1111/tpj.14276 [DOI] [PubMed] [Google Scholar]
  • 3. : Fungal and plant gene expression in the Tulasnella calospora-Serapias vomeracea symbiosis provides clues about nitrogen pathways in orchid mycorrhizas. New Phytol .2017;213(1) : 10.1111/nph.14279 365-379 10.1111/nph.14279 [DOI] [PubMed] [Google Scholar]
  • 4. : Genomes of leafy and leafless Platanthera orchids illuminate the evolution of mycoheterotrophy. Nat Plants .2022;8(4) : 10.1038/s41477-022-01127-9 373-388 10.1038/s41477-022-01127-9 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 5. : Structure and development of orchid mycorrhizas.2016; 10.1002/9781118951446.ch5 63-86 10.1002/9781118951446.ch5 [DOI] [Google Scholar]
  • 6. : Mycorrhizal networks: des liaisons dangereuses?. Trends Ecol Evol .2006;21(11) : 10.1016/j.tree.2006.07.003 621-8 10.1016/j.tree.2006.07.003 [DOI] [PubMed] [Google Scholar]
  • 7. : Seasonal and environmental changes of mycorrhizal associations and heterotrophy levels in mixotrophic Pyrola japonica (Ericaceae) growing under different light environments. Am J Bot .2012;99(7) : 10.3732/ajb.1100546 1177-88 10.3732/ajb.1100546 [DOI] [PubMed] [Google Scholar]
Open Res Eur. 2023 Dec 22. doi: 10.21956/openreseurope.17913.r35973

Reviewer response for version 1

Jason D Hoeksema 1

We welcome the contribution of this paper to the discussion about how to interpret results of experiments on common mycorrhizal networks (CMNs). However, we disagree that ‘factual evidence about belowground C transfer across CMNs is solid and accumulating.’ There is currently too much uncertainty in interpretation of approved research to make such statements. The authors themselves imply this in the answers they provide to their five questions. In those answers the authors describe many factors that make interpretation of earlier results complicated. As just one example, when discussing Question 1, the authors conclude:

'The ecological significance of C transfer among different tree species can be masked by the complexity of host tree roots and CMNs.'

We agree that the ecological significance of C transfer of CMNs is difficult to determine; however, that does not mean that we can assume that the ecological significance is high. It could just as likely be low. We simply do not know.

Below, we raise additional questions about interpretations of past experiments and highlight how they are not conclusive evidence for the transfer of carbon (C) through CMNs. We agree with the authors that further research is needed in this area. Indeed, the conclusion of the Karst et al. (2023) review was that far more research is needed on the function of CMNs in forests, given the many confounding factors in field experiments on CMNs. Therefore, we recommend that the title of the current paper be revised to “Belowground carbon transfer across mycorrhizal networks among trees: A possibility worthy of further investigation”

Abstract:

‘Carbon (C) transfer across a common mycorrhizal network (CMN) was demonstrated … later in the field (Simard et al. 1997).’

We agree that C moved belowground in the experiment by Simard et al. (1997), but whether it was through a CMN is inconclusive for the reasons explained in Karst et al. (2023) and Henriksson et al. (2023).

‘…including evidence for ecological significance of carbon transfer (Klein et al. 2016).’

First, the Klein et al. (2016) study attempted to estimate the quantity of C transferred through CMNs, but did not attempt to measure the consequences of such C transfer for the growth, survival, or other metric of plant fitness or performance, which would be important for demonstrating the "ecological significance" of carbon transfer.

Moreover, there are a number of unresolved issues in Klein et al. (2016) precluding conclusive interpretations on the amounts and the belowground pathways of C movement:

a) Would the high concentration of CO 2 (mean 530-590 ppm) applied to the labelled trees inflate the amount of C transferred belowground? As Henriksson et al. (2023) point out, it is possible that the donor trees had enhanced capacity to fix C and export photosynthates to their mycorrhizal mycelium, and hence potentially to other trees.

b) Did the ‘controls’ actually account for the soil pathway of C transfer? Klein et al. (2016) rely on two results to conclude that there was no C moving via the soil pathway (e.g., turnover of litter by soil biota and the subsequent redistribution of its C, and transport in soil water by diffusion and mass flow). First, they compared δ 13C  in saprotrophic versus mycorrhizal sporocarps and reported zero δ 13C labeling in saprotrophic fungi and decreasing mycorrhizal δ 13C  with decreasing distance from the labeled Picea. However, the isotopic signatures of  sporocarps and roots cannot be compared because the sporocarps had been sampled four years prior to the roots. Specifically, sporocarps were sampled one to two years after labelling was initiated (2010 & 2011) (Mildner et al. 2014) and fine roots were sampled five and six years after labelling commenced (2015) (Klein et al. 2016). Had the sporocarps been sampled in 2015 along with the fine roots, it is quite likely that some label would have shown up in the saprotrophic species. The lack of change in δ 13C  in saprotrophs at increasing distances from labelled trees (averaged across distances in Klein et al. (2016), Fig. 1) may be an artefact of sampling time and not necessarily an indication that C does not move through the soil pathway. Furthermore, the sporocarps were sampled from different locations than the roots (i.e., from different distances around a single labelled tree, not from around labelled and unlabelled trees).

Second, they sampled δ 13C in rhizomes of arbuscular mycorrhizal (AM) understory plants, compared it to the fine roots of labelled/adjacent roots of ectomycorrhizal (EM) canopy trees, and reported that ‘there was absolutely no signal difference between samples collected around unlabelled and labelled Picea, and no difference between years.’ Would we expect underground stems (rhizomes) to take up C compounds from the soil in the same amounts as would fine roots of canopy trees? The rhizomes of the understory plants were peeled to remove the bark before analysis, and this would have removed any fine roots present.

One other issue to consider that we and Henriksson et al. (2023) point out in our reviews, is that the higher label intensity in EM plants could be due to more effective scavenging of labeled compounds because of greater hyphal density compared with the AM plants. So, is the absence of label in rhizomes of an AM understory plant a robust control for the soil pathway?

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).'

Diffusion and mass flow are two separate mechanisms for solute movement in soil, but their rates differ substantially. The authors should clarify which they are referring to, although mass flow is likely more important, given that rates can be much faster than diffusion. Diffusion rate will vary depending on the type of solute. A rate of m per month -1 could explain a substantial proportion of long-distance movement of organic molecules in the field.

It is notable that Avital et al. (2022) acknowledge, when referring to diffusion, that “ Several cases of carbon transfer demonstrated in our results certainly fit these dynamics, …”, while concluding that other results were better explained by a faster mechanism, such as transport through CMNs. The authors of the current paper do not acknowledge this caveat.

‘…CMN-C transfer from mature trees to seedlings has been demonstrated (Orrego 2018)’.

To summarize Oreggo (2018), an MSc thesis from the University of British Columbia, eight 'mother' hemlock trees were selected, and a fallen log within 10 m was identified around each tree. Naturally regenerated hemlock seedlings were growing on the logs. A portion of each log, i.e., a ‘control’, was cut and placed on some boards (to severe CMN connections from ‘mother’ trees). 13C-labelled glucose was injected into the phloem of each ‘mother’ tree. On days 9 and 15, seedlings on intact and raised logs and the forest floor were analyzed for 13C enrichment. Seedlings on intact logs and the forest floor were enriched. There was no significant enrichment of 13C for seedlings growing on control logs. In the thesis and in the book 'Finding the Mother Tree’ (Simard 2021), these results are interpreted as ‘mother’ trees providing carbon to their seedlings through CMNs. However, cutting logs and raising them onto boards would not only disconnect CMNs between seedlings and adjacent trees, it would also disrupt the soil pathway. It is not possible to conclude that CMNs mediate C transfer with this experimental set-up, as there was no control for the soil pathway.

‘…have suggested that trees in forests are more connected than once thought (Simard 2021).’

This book is a non-peer-reviewed memoir; therefore, it is not an appropriate source to be cited for scientific evidence in this paper. And as Robinson et al. (2023) point out, there are several misleading claims regarding CMNs in the book.

Plain language summary:

‘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 Cahanovitc et al. (2022), there is no treatment to control for C transferred through root exudates. The ‘control’ treatment prevents the formation of both CMNs and C transfer through soil solution. The ‘treatment’ allows for CMN formation and C transfer through soil solution. Unfortunately, the mechanisms are confounded in this set-up. Passive diffusion may be slow but the distance between hyphae extending from mycorrhizal root tips is likely to be very small. That is, it is not the distance between root tips that is relevant, it is the distance between the tips of hyphae colonizing roots that matters. Other experiments testing the effects of CMNs on C transfer have shown that CMNs are not essential for belowground C transfer to occur (e.g., Simard et al. 1997a, Teste et al. 2010, Pickles et al. 2016). That is, even in the absence of CMNs, C moves belowground, providing evidence for the soil pathway.  

‘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.’

In the abstract of Simard et al. (1997a) it states ‘Neither net nor bidirectional transfer differed between severing treatments, leaving in question the relative importance of EM hyphae versus soil transfer pathways.’ Thus, this study is not conclusive evidence for C moving through CMNs. Perhaps the authors meant to refer to Simard et al. 1997b?

‘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).’

In Sapes et al. (2021), the CMN treatments didn’t work as planned, so there was no comparison between seedlings with and without CMNs. In Song et al. (2015), a pot study, there is evidence of C transfer through CMNs, and for subsequent upregulation of potential defensive enzymes, but both of those effects are negated when roots are allowed to intermingle, as they would in a real forest. This is a fascinating result, but is the only experiment testing this mechanism in trees, and does not support stating that CMN-mediated C transfer would have ecological significance in a real forest.

‘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...’

The idea of kin vs non-kin (i.e., whether donor and recipient trees/saplings/seedlings are genetically related) is being confused here with whether the donor and recipient trees/saplings/seedlings were of the same or different species. The meaning should be clarified.

Neither of the studies cited used a shading treatment, and neither considered the genetic relatedness of the donors and receivers. Both were performed in logged sites, so all seedlings were sunlit. Most importantly, neither of these studies investigated C transfer, only effects of CMNs on seedling survival and other characteristics.

Bingham and Simard (2012) found that ‘Seedling survival decreased when seedlings were unable to form a network’. However, alternative interpretations are (i) that the soil volume available to foraging hyphae was smallest in the 0.5 µm mesh treatment, thereby reducing seedling survival in the control treatment, or (ii) that the mesh treatments altered the composition or diversity of the EM fungal community (as found by Teste et al. 2009a & 2009b) or pathogenic fungal communities in ways that affected seedling survival.

‘C transfer takes place between different, unrelated tree species sharing mycorrhizal species (Avital et al., 2022; Rog et al., 2020).’

Rog et al. (2020) provides good support for C transfer from trees to EM fungi. However, we question that the magnitude of belowground C transfer was correlated with EM fungal community similarity, as the analyses on which this claim was based eliminated noise by averaging within species and by dropping extreme values from what was already a small data set. We also note that in Avital et al. (2022), there was no significant correlation between the δ 13C level in the recipients and the abundance of mycorrhiza fungal ASVs shared with the donor tree. Altogether, it doesn’t appear that the relationship between EM fungal community similarity and C transfer is clear across these two studies.

‘This includes C transfer between an EM-host to an AM-host with dual mycorrhization status (Cupressus sempervirens; Avital et al., 2022).’

Was it confirmed that Cupressus sempervirens was colonized by both ecto- and arbuscular mycorrhizal fungi in the experiment? Without these data, we agree with Henriksson et al. (2023): that C transfer in this study most likely occurred via non-mycorrhizal pathways.

Other issues:

'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).'

References should be provided for this statement. We are not away of studies that have shown that the Hartig net degenerates and provides C to EM plants.

'However, there is sufficient evidence that trees in forests are connected by a CMN and transmitting C among themselves, …'

We agree that it is likely that many trees in forests are connected by CMNs, but we disagree that there is currently sufficient evidence for this statement. Detailed mapping of fungal genets and their mycorrhizal roots using genotyping tools has been conducted in only two tree species, and the temporal dynamics and persistence of CMNs has not been explored, so much more research is required.

We agree that there is sufficient evidence that C moves belowground between trees. The current sentence structure does not imply that the C is moving through the CMNs, which is appropriate; however, this could be missed during a quick read of the sentence. We recommend that the sentence be re-written so that readers are not confused on the meaning here. Yes, C can move belowground, and, yes, it is likely that some roots of trees are physically connected by a mycorrhizal fungal mycelium; however, linking those two in a functional way is premature.

Where applicable, are recommendations and next steps explained clearly for others to follow? (Please consider whether others in the research community would be able to implement guidelines or recommendations and/or constructively engage in the debate)

Not applicable

Does the article adequately reference differing views and opinions?

Yes

Are all factual statements correct, and are statements and arguments made adequately supported by citations?

Partly

Is the rationale for the Open Letter provided in sufficient detail? (Please consider whether existing challenges in the field are outlined clearly and whether the purpose of the letter is explained)

Yes

Is the Open Letter written in accessible language? (Please consider whether all subject-specific terms, concepts and abbreviations are explained)

Yes

Reviewer Expertise:

Ecology and evolution of mycorrhizal symbiosis; experimental approaches to studying common mycorrhizal networks

I confirm that I have read this submission and believe that I have an appropriate level of expertise to confirm that it is of an acceptable scientific standard, however I have significant reservations, as outlined above.

References

  • 1. : Asymmetric belowground carbon transfer in a diverse tree community. Mol Ecol .2022;31(12) : 10.1111/mec.16477 3481-3495 10.1111/mec.16477 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 2. : Ectomycorrhizal Networks of Pseudotsuga menziesii var. glauca Trees Facilitate Establishment of Conspecific Seedlings Under Drought. Ecosystems .2012;15(2) : 10.1007/s10021-011-9502-2 188-199 10.1007/s10021-011-9502-2 [DOI] [Google Scholar]
  • 3. : Ectomycorrhizal fungi mediate belowground carbon transfer between pines and oaks. ISME J .2022;16(5) : 10.1038/s41396-022-01193-z 1420-1429 10.1038/s41396-022-01193-z [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 4. : Re-examining the evidence for the mother tree hypothesis - resource sharing among trees via ectomycorrhizal networks. New Phytol .2023;239(1) : 10.1111/nph.18935 19-28 10.1111/nph.18935 [DOI] [PubMed] [Google Scholar]
  • 5. : Positive citation bias and overinterpreted results lead to misinformation on common mycorrhizal networks in forests. Nat Ecol Evol .2023;7(4) : 10.1038/s41559-023-01986-1 501-511 10.1038/s41559-023-01986-1 [DOI] [PubMed] [Google Scholar]
  • 6. : Belowground carbon trade among tall trees in a temperate forest. Science .2016;352(6283) : 10.1126/science.aad6188 342-4 10.1126/science.aad6188 [DOI] [PubMed] [Google Scholar]
  • 7. : Long-term ¹³C labeling provides evidence for temporal and spatial carbon allocation patterns in mature Picea abies. Oecologia .2014;175(3) : 10.1007/s00442-014-2935-5 747-62 10.1007/s00442-014-2935-5 [DOI] [PubMed] [Google Scholar]
  • 8. : Transfer of 13 C between paired Douglas-fir seedlings reveals plant kinship effects and uptake of exudates by ectomycorrhizas. New Phytol .2017;214(1) : 10.1111/nph.14325 400-411 10.1111/nph.14325 [DOI] [PubMed] [Google Scholar]
  • 9. : Mother trees, altruistic fungi, and the perils of plant personification. Trends Plant Sci .2023; 10.1016/j.tplants.2023.08.010 10.1016/j.tplants.2023.08.010 [DOI] [PubMed] [Google Scholar]
  • 10. : Share the wealth: Trees with greater ectomycorrhizal species overlap share more carbon. Mol Ecol .2020;29(13) : 10.1111/mec.15351 2321-2333 10.1111/mec.15351 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 11. : Plant carbohydrate depletion impairs water relations and spreads via ectomycorrhizal networks. New Phytol .2021;229(6) : 10.1111/nph.17134 3172-3183 10.1111/nph.17134 [DOI] [PubMed] [Google Scholar]
  • 12. : Reciprocal transfer of carbon isotopes between ectomycorrhizal Betula papyrifera and Pseudotsuga menziesii. New Phytol .1997;137(3) : 10.1046/j.1469-8137.1997.00834.x 529-542 10.1046/j.1469-8137.1997.00834.x [DOI] [PubMed] [Google Scholar]
  • 13. : Net transfer of carbon between ectomycorrhizal tree species in the field. Nature .1997;388(6642) : 10.1038/41557 579-582 10.1038/41557 [DOI] [Google Scholar]
  • 14. : Defoliation of interior Douglas-fir elicits carbon transfer and stress signalling to ponderosa pine neighbors through ectomycorrhizal networks. Sci Rep .2015;5: 10.1038/srep08495 8495 10.1038/srep08495 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 15. : Access to mycorrhizal networks and roots of trees: importance for seedling survival and resource transfer. Ecology .2009;90(10) : 10.1890/08-1884.1 2808-22 10.1890/08-1884.1 [DOI] [PubMed] [Google Scholar]
  • 16. : Role of mycorrhizal networks and tree proximity in ectomycorrhizal colonization of planted seedlings. Fungal Ecology .2009;2(1) : 10.1016/j.funeco.2008.11.003 21-30 10.1016/j.funeco.2008.11.003 [DOI] [Google Scholar]
  • 17. : Net carbon transfer betweenPseudotsuga menziesii var.glauca seedlings in the field is influenced by soil disturbance. Journal of Ecology .2010;98(2) : 10.1111/j.1365-2745.2009.01624.x 429-439 10.1111/j.1365-2745.2009.01624.x [DOI] [Google Scholar]
Open Res Eur. 2023 Oct 12. doi: 10.21956/openreseurope.17913.r35510

Reviewer response for version 1

David Perry 1

The article is an important contribution to the debate on C movement in common mycorrhizal networks (CMN). Recent publications (e.g. Karst et al., cited by the authors of this paper) have raised significant questions about that phenomenon. Most points raised by Karst and others are correct, but unfortunately they have also effectively thrown the baby out with the bathwater, denying what has been demonstrated in numerous published papers. It is important to set the record straight on what is known and what is not, and Klein et al. do a good job of that. The question of resource transfer through CMNs may or may not have significant implications for forest growth and health. I think it does, but to move research ahead efficiently we need to acknowledge the potential that has been shown, and we now need to know why it manifests sometimes/places and not others. I wholeheartedly endorse the Klein et al. manuscript.

Specific comments:

Point 5. “ t ransfer 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).” A couple of points need clarification: 1) "going both ways” - That seems to imply the plant can transfer amino acids to the fungus. Is that what you intend? If so, provide a citation. (2) “(as in AMF arbuscules)” - I believe what you intend to say is “plants acquire C from degenerating hyphae in the Hartig Net or in AMF arbuscules”.

Finally, an evolutionary advantage should exist for fungi to maintain diversity of tree hosts and hence C sources ( Tedersoo et al., 2020)” I’d note this argument was made by Perry (1998 1 ).

Where applicable, are recommendations and next steps explained clearly for others to follow? (Please consider whether others in the research community would be able to implement guidelines or recommendations and/or constructively engage in the debate)

Yes

Does the article adequately reference differing views and opinions?

Yes

Are all factual statements correct, and are statements and arguments made adequately supported by citations?

Yes

Is the rationale for the Open Letter provided in sufficient detail? (Please consider whether existing challenges in the field are outlined clearly and whether the purpose of the letter is explained)

Yes

Is the Open Letter written in accessible language? (Please consider whether all subject-specific terms, concepts and abbreviations are explained)

Yes

Reviewer Expertise:

Ecological processes. Ecology of mycorrhizal fungi

I confirm that I have read this submission and believe that I have an appropriate level of expertise to confirm that it is of an acceptable scientific standard.

References

  • 1. : A moveable feast: the evolution of resource sharing in plant-fungus communities. Trends Ecol Evol .1998;13(11) : 10.1016/s0169-5347(98)01456-6 432-4 10.1016/s0169-5347(98)01456-6 [DOI] [PubMed] [Google Scholar]
Open Res Eur. 2023 Oct 13.
tamir klein 1

Dear Prof. David Perry (Reviewer 1), Thank you for your positive assessment of our letter. We appreciate the comments made and will adjust the letter accordingly, once the other additional review reports come in. Sincerely, Tamir Klein

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