Investigation of Plant Interactions Across Common Mycorrhizal Networks Using Rotated Cores

Joanna Weremijewicz; David  P. Janos

doi:10.3791/59338

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Investigation of Plant Interactions Across Common Mycorrhizal Networks Using Rotated Cores

Published: March 26, 2019

doi:

10.3791/59338

Joanna Weremijewicz^1,2, David P. Janos²

¹Department of Biology,North Central College, ²Department of Biology,University of Miami

Summary

Most plants within communities likely are interconnected by arbuscular mycorrhizal (AM) fungi, but mediation of plant interactions by them has been investigated primarily by growing plants with versus without mycorrhizas. We present a method to manipulate common mycorrhizal networks among mycorrhizal plants to investigate their consequences for plant interactions.

Abstract

Arbuscular mycorrhizal (AM) fungi influence plant mineral nutrient uptake and growth, hence, they have the potential to influence plant interactions. The power of their influence is in extraradical mycelia that spread beyond nutrient depletion zones found near roots to ultimately interconnect individuals within a common mycorrhizal network (CMN). Most experiments, however, have investigated the role of AM fungi in plant interactions by growing plants with versus without mycorrhizal fungi, a method that fails to explicitly address the role of CMNs. Here, we propose a method that manipulates CMNs to investigate their role in plant interactions. Our method uses modified containers with conical bottoms with a nylon mesh and/or hydrophobic material covering slotted openings, ¹⁵N fertilizer, and a nutrient-poor interstitial sand. CMNs are left either intact between interacting individuals, severed by rotation of containers, or prevented from forming by a solid barrier. Our findings suggest that rotating containers is sufficient to disrupt CMNs and prevent their effects on plant interactions across CMNs. Our approach is advantageous because it mimics aspects of nature, such as seedlings tapping into already established CMNs and the use of a suite of AM fungi that may provide diverse benefits. Although our experiment is limited to investigating plants at the seedling stage, plant interactions across CMNs can be detected using our approach which therefore can be applied to investigate biological questions about the functioning of CMNs in ecosystems.

Introduction

Arbuscular mycorrhizal (AM) fungi assisted plants in the colonization of land 460 million years ago¹ and today, they are ubiquitous symbionts of most plants², providing them with vital mineral nutrients for growth. The thin, thread-like hyphae of AM fungi forage for mineral nutrients beyond nutrient depletion zones near roots, often encountering and colonizing root systems of neighboring plants in a “common mycorrhizal network” (CMN). Common mycorrhizal networks also may form when fungal germlings join established networks³, or when AM hyphae fuse (anastomose) with conspecific hyphae⁴^,⁵^,⁶^,⁷. The extent of these extraradical hyphae in the soil is enormous, with extraradical hyphae constituting 20% to 30% of total soil microbial biomass in prairie and pasture soils⁸ and stretching for 111 m·cm^-3 in undisturbed grassland⁹.

Common mycorrhizal networks partition mineral nutrients among interconnected neighboring plants¹⁰^,¹¹^,¹²^,¹³. Plants may receive up to 80% of their phosphorus and 25% of their nitrogen requirements from AM fungi, while providing up to 20% of their total fixed carbon to the fungi in return¹⁴. Recent in vitro root organ culture work has found that CMNs preferentially exchange mineral nutrients with host roots that provide the most carbon to the fungi¹¹^,¹². Furthermore, different species of AM fungi may differ in their quality as symbiotic partners, with some fungi exchanging more phosphorus for less carbon than others¹⁵. Although root organ cultures are beneficial models for studying the AM symbiosis because they present carefully controlled environments and the ability to directly observe hyphal interconnections, they do not include photosynthesizing shoots which affect important physiological processes such as photosynthesis, transpiration, and diurnal changes, as well as constituting carbon and mineral nutrient sinks.

In nature, seedlings most likely tap into already established CMNs. Until recently, however, scientists have only examined the impact of AM fungi on plant nutrition by growing plants with and without AM fungi, often with a single species of AM fungus. Although this work has been tremendously informative to our understanding of arbuscular mycorrhizas, this method has overlooked the potentially crucial role that CMNs may have in interactions among interconnected host plants. In particular, plants that are highly dependent on AM fungi for growth interact minimally without AM fungi¹⁶^,¹⁷, possibly confounding our interpretation of AM fungus-mediated interactions when used as ‘controls’ for baseline reference.

We propose a rotated-core approach for investigation of the role of CMNs in plant interactions and population structuring. Our approach mimics components of the AM symbiosis in nature because whole plants join established CMNs and all plants are grown with AM fungi. By removing root interactions, our methodology specifically focuses on interactions mediated by AM fungi while also tracking mineral nutrient movement within CMNs. Our approach builds on previous work that has used rotated cores both in the field and in the greenhouse to understand AM functioning realistically.

The rotated core method has been established in the literature as a method to manipulate extraradical hyphae¹⁸^,¹⁹^,²⁰^,²¹, and it has had several reincarnations depending on its purpose over the past two decades. Initially, mesh bags or barriers allowing in-growth of hyphae were used to provide root-free compartments to quantify the amount of arbuscular mycorrhizal hyphae in the soil²²^,²³. Then, cylindrical cores of soil enclosed in rigid water pipes or plastic tubing with slots covered in a nylon mesh penetrable by hyphae, but not roots, were developed. These could easily be rotated to disrupt extraradical mycelia¹⁸^,²⁴^,²⁵. The rotated cores were placed between plants, and soil hyphal lengths per gram of soil¹⁸, ¹³C fluxes to extraradical mycelia²⁴, or phosphorus uptake from plant-free cores were quantified¹⁸. Another use of such cores was to grow plants within them in the field to reduce colonization of roots by AM fungi through frequent hyphal disruption as an alternative to sterilization or the application of fungicides, both of which have indirect effects on soil organic matter and other microbes¹⁸.

The hyphal mesh barrier approach has been used to investigate nutrient partitioning and plant interactions across CMNs, but in rectangular microcosms rather than with rotated cores. Walder et al.²⁶ investigated interactions between Linum usitatissimum (flax) and Sorghum bicolor (sorghum) by tracing mineral nutrient for carbon exchange using isotopes across CMNs of either of the AM fungi Rhizophagus irregularis or Funneliformis mosseae²⁶. The microcosms in their study comprised plant compartments separated by mesh barriers, hyphal compartments only accessible to mycorrhizal hyphae, and labeled hyphal compartments that contained radioactive and stable isotopes. As controls, the study used treatments without mycorrhizal fungi. Song et al.²⁷ used a similar approach to find that plant signals could be carried only among established CMNs of F. mosseae when one plant was infected by a fungal pathogen. Also, similarly to Walder et al.²⁶, Merrild et al.²⁸ grew plants in individual compartments separated by mesh to investigate plant performance of Solanum lycopersicum (tomato) seedlings linked by CMNs to a large Cucumis sativus (cucumber) plant that represented an abundant carbon source. They also used treatments without mycorrhizal fungi instead of severing CMNs²⁸. In a second, related experiment, carbon for phosphorus exchange was examined using mesh bags labeled with ³²P. Microcosms with hyphal mesh barriers and CMN severing as a treatment were used by Janos et al.²⁹, who investigated competitive interactions between seedlings of the savanna tree species Eucalyptus tetrodonta and transplants of the rain forest tree, Litsea glutinosa. In that study, Janos et al.²⁹ lifted compartments containing seedlings a few centimeters, sliding layers of mesh against one another to break hyphal interconnections²⁹.

The final step in the evolution of the rotated core method has been to grow plants inside cores that are within pots or microcosms²⁰^,³⁰. Wyss³⁰ used rotated cores to ascertain if extraradical AM mycelium could colonize Pinus elliottii seedlings when spreading from a donor or ‘nurse’ AM host plant, Tamarindus indica, and how extraradical mycelium of ectomycorrhizal fungi influences seedling performance. Large commercial tubular seedling containers (Table of Materials) within microcosms were either solid plastic (no CMNs) or slotted and covered with a hydrophobic membrane. Slotted seedling containers were either not rotated (intact CMNs) or rotated to sever established CMNs. Rotated cores with different mesh barrier sizes were used by Babikova et al.²⁰ to investigate belowground signaling through CMNs among Vicia faba (bean) plants. In their study, a central donor plant in 30 cm diameter mesocosms was interconnected either by roots and hyphae (no barrier) or only by CMNs established through a 40 μm mesh. Central plants were severed from interactions with neighboring plants through rotation of the mesh-enclosed cores, or CMNs were prevented by a fine 0.5 μm mesh enclosing the core.

Here, we present a method that combines aspects of prior rotated-core approaches to examine the influence of CMNs on direct plant interactions combined with stable isotope tracing. Our method uses a ‘target plant’ approach, in which the central plant of interest is surrounded by neighboring plants. Plants are grown inside rotatable seedling containers that are slotted and covered with nylon silk-screen mesh, hydrophobic membrane, or are non-modified solid plastic. Common mycorrhizal networks are severed once a week or kept intact, and ¹⁵N stable isotopes trace the movement of nitrogen from neighbors’ rotated cores to the central target plant. By comparing plant size with mineral nutrient and stable isotope uptake, we assess which plants may benefit or suffer from CMNs in interactions among host plants.

Protocol

1. Construction and assembly of rotatable cores

Modify commercial tubular seedling containers (subsequently called ‘containers’; Table of Materials) to have 19 mm wide x 48 cm length openings.
1. Using a drill-press with a 19 mm hole saw without a central, pilot twist drill, cut two holes, one above the other, in the sides of a container (2.5 cm diameter x 12.1 cm length) so that the holes are about 1 cm apart. Hold the container against a fence on the drill press and have a stop with a short dowel that will fit inside the container to help hold it in place while drilling. Use a container with flexible plastic to prevent cracking.
2. Cut the remaining thin piece of plastic between the holes with scissors, a wire cutter, or tin snips (for rigid plastic use a sabre-saw) to make one elongated opening about 2 cm wide and 5 cm long.
3. Repeat steps 1.1.1 – 1.1.2 on the opposite side of the container.
Cover the slots with nylon mesh and/or hydrophobic membrane (Figure 1A).
1. Cut nylon mesh with 40 μm pores into 9.5 cm x 8.5 cm pieces. Cut as many pieces as there are containers.
2. Glue the nylon mesh externally onto the containers to cover both openings with some slight overlap in the fabric using high-strength, industrial hot glue.
3. If the prevention of water movement is needed, such as when using water-soluble nutrients or stable isotopes, cover the nylon mesh layer with a hydrophobic membrane³¹^,³² (Table of Materials) that allows AM fungus hyphae to pass, but only the movement of water vapor and not liquid water.
4. Place the hot glue around the openings on the container and along the long edges of the nylon mesh. Roll the container onto the fabric to avoid burning fingers. Add a layer of glue along the fabric edge where the mesh edges overlap. Press the edge onto some cardboard to firmly seal it. Always roll consistently in one direction that will be the same direction of the rotation of the finished containers within pots or microcosms so that the overlapped mesh edge will not be pushed to potentially dig into the substrate.
5. Once the glue has cooled, tape the top and bottom ends of the fabric to the container to prevent loose edges and ripping using a flexible tape, such as electrician's tape.
Using the same tape as in step 1.2.5, cover the small holes on the sides of the conical end (not the hole at the tip of the bottom) of each container to prevent root growth out of the container into the rest of the pot/microcosm.
To prevent soil loss while providing drainage, place a glass marble into the bottom of each container.
For a control treatment that does not involve any potential for a CMN to form between plants, use solid, unmodified containers (Figure 1A).

2. Assembly of pots or microcosms to fit the conical ends of the containers

To ensure containers stand upright in a fixed position and have proper drainage, flip a pot over so that the bottom is facing up. Cut around the bottom of the pot, leaving a small lip for support, using a sabre-saw.
Preparation of polystyrene foam
1. Cut polystyrene foam, about 36 mm thick, to the same diameter as the bottom of the pot using a bandsaw with a circle-cutting jig.
2. Drill holes into the foam using a drill press and 19 mm hole saw (without a central twist drill) in the pattern in which the containers will be positioned.
3. For a target plant experiment, drill a central hole with equally spaced holes for neighboring individuals surrounding it. For a pot with a 15.5 cm diameter, space six holes 12 mm apart around the circumference of an 11 cm diameter circle (Figure 1B).
4. Lay out the holes hexagonally or in a square array (Figure 1C, D) for a microcosm experiment.

3. Filling of the containers and pots with soil and sand mixtures

Select a desired soil mixture and add AM fungus field-collected or pot-cultured inoculum to the soil by uniformly mixing chopped root pieces (1 – 2 cm long) thoroughly with the soil. Mix the desired soil with an infertile silica sand or glass beads to decrease the concentration of mineral nutrients available to plants.
Position the filled containers in the drilled foam or microcosm bottom and fill the interstitial space with an infertile substrate.
Fill the interstitial space between containers with nutrient-poor silica sand mixture using a funnel to assist in filling small spaces. To ensure adequate drainage and mimic the texture of the soil, mix medium particle-size sand, such as 6-20 grade, with small particle-size sand, such as 30-65 grade, in a cement mixer.

4. Establishment of CMNs throughout pots/microcosms

Plant pretreatment ‘nurse’ plants of the desired species into each container to sustain AM fungi so that they can spread among the containers and establish CMNs.
When all containers have established seedlings, remove shoots by clipping so that only one individual remains in each container.
Allow 2-3 months for plant growth and CMN establishment.

5. Establishment of experimental plants and treatments

Sow experimental plants by seeding or transplanting into containers. If seeding, wait until all containers have a germinated seedling before removing pre-treatment nurse plants by clipping their shoots. If transplanting, clip all pre-treatment plants before transplanting experimental seedlings to prevent unintended competitive effects.
Establish CMN treatments by either leaving the containers not moved for the duration of the experiment (intact CMNs) or rotating them weekly to physically sever hyphae extending among the modified containers (severed CMNs; Figure 1A). When severing CMNs, rotate each container through one full rotation to avoid unintentionally altering aboveground interactions, particularly for heliotropic plants.
Heavily water all pots or microcosms immediately after rotation to reestablish contact between the interstitial substrate and the sides of containers.

6. Tracing of mineral nutrient movement across CMNs

Fertilize neighboring plants with 0.5% ¹⁵N enriched KNO₃ and NH₄Cl.
Fertilize the target individual with a ¹⁴N fertilizer of equal concentration.

7. Monitoring and maintenance of experiment

Regularly (at least monthly) re-randomize the positions of the pots or microcosms over the course of the experiment.
Weekly measure growth, such as height or longest leaf length (for grasses) to monitor when growth begins to slow, because it is important to harvest before the plants become root-bound.

8. Harvest of the experiment

Clip all aboveground tissue and place individual plants into labeled envelopes that identify their treatment, pot or microcosm, and position.
Dry aboveground tissues at 60 °C to constant weight. Measure the dry weight of each plant tissue.
Allow the soil to dry before extracting the containers and harvesting the roots.
Delicately brush off as much soil as possible from the root systems and wash them in a pan of water or under a gentle stream of water on a sieve of 250 micron pore size.
Allow the roots to air-dry and weigh the whole root system.
Clip the root system haphazardly and store the root fragments in 50% ethanol. After they are stained³³, use these fragments for quantification of root colonization using the gridline intersection method³⁴.
Re-weigh the remaining root system and store it in a labeled paper envelope to dry at 60 °C for assessment of dry weight. Use the following equation to calculate the weight of the entire root system:

9. Mineral nutrient and stable isotope analyses

Group the seedlings by biomass into “deciles” or 10 groups, “octiles” or 8 groups, “quartiles” or four groups, etc. after rank-ordering them by weight if the tissue quantity is too low for minimum requirements for digestion to determine mineral nutrient concentrations.
Send foliar samples to a contracted lab for mineral nutrient and stable isotope analyses (Table of Materials).
1. Describe isotopic abundance using the following customary expression:
  
  where R represents the ¹⁵N/¹⁴N ratio of a sample or of the standard which is atmospheric N.
2. Use the non-modified, solid container treatment to serve as a control for background ¹⁵N ratios in the following mass balance equation when quantifying the amount of ¹⁵N taken up by a target plant in severed or intact CMN treatments:
  
  where δ¹⁵N represents the isotopic abundance of targets, neighbors, and target plants in the no CMN treatment, and x represents (as a decimal fraction) the percent nitrogen obtained by the target plant from neighbor containers to which label was added. Values for δ¹⁵N_Neighbors are obtained for each target plant’s composited neighbors.

Representative Results

To determine how CMNs may influence plant performance through nutrient partitioning, we grew Andropogon gerardii Vitman, a dominant prairie grass, in a target plant experiment with 6 equally spaced neighbors and intact, severed, or no CMNs. We found that severing or preventing CMNs diminished targets’ aboveground dry weights (Figure 2), suggesting that intact CMNs promoted plant growth. Plants with severed CMNs and prevented CMNs responded notably similarly to their treatments, suggesting that the rotation of containers once a week was successful in mitigating the effects of CMNs. The severed CMN treatment, however, may be preferred as a control because the nylon mesh (which was overlain by a hydrophobic membrane in this experiment) in both intact and severed treatments may affect water dynamics such as the soil of slotted containers (rotated or not) drying more quickly than that in non-modified containers.

Competition, in which the growth of one individual suppresses the growth of another nearby individual, was detected in the intact CMN treatment but not in the severed or no CMNs treatments. We found that only when CMNs were intact did target and summed neighbor sizes have a negative relationship as demonstrated by linear regression (Figure 3). The severed and no CMNs treatments did not differ from one another, and together, their slopes did not differ significantly from zero. Hence, they significantly differed from the negative slope of the intact CMNs treatment (Figure 3). Furthermore, we found that Gini coefficients, a measure of size inequality that ranges from zero to one in which zero reflects a perfectly equal size distribution, differed among treatments. The intact CMNs treatment had the greatest inequality¹⁰^,³⁵^,³⁶. Size inequalities are affected by competition within populations, particularly when large individuals dominate resource acquisition, thereby disproportionally suppressing the growth of small individuals, also known as asymmetric competition³⁷^,³⁸.

Whether mineral nutrients were growth-limiting, and if CMNs contributed to intensifying competition for those nutrients was determined through comparisons of mineral nutrient leaf tissue concentrations versus plant size. Of all the mineral nutrients assessed, we found that only Mn leaf tissue concentrations were positively associated with target plant aboveground dry weights over all treatments, with no significant differences among slopes, suggesting that Mn may have limited growth among all treatments (Figure 4). Nevertheless, regression line elevations, which suggest differences in mean concentrations among treatments, were affected by CMN severing and prevention. Mean foliar N concentrations were not significantly affected by CMN treatments, but N concentration significantly decreased with aboveground dry weight of target plants, suggesting a potential ‘dilution effect’ of plant size on tissue N³⁹^,⁴⁰. Therefore, N was not likely the growth-limiting mineral nutrient in our experiment. In another similar experiment, mean foliar P was significantly affected by CMN treatment, but also showed a dilution effect when compared to plant size for plants with intact CMNs³⁵.

To examine if CMNs differentially partition mineral nutrients among interconnected individuals, we assessed target plant tissue for ¹⁵N in leaf tissues versus plant size. We had added ¹⁵N-label only to neighbors’ containers. We found that target plants with intact CMNs had higher ¹⁵N concentrations compared to both other treatments, which did not differ from one another (Figure 5A). Although target aboveground dry weight was associated with the amount of nitrogen obtained from neighbors’ containers over both intact and severed CMNs treatments, intact CMNs had a strongly positive, significantly different slope from that of the severed CMNs treatment (Figure 5B). These results suggest that large plants, potentially with abundant photosynthate, obtained more ¹⁵N from CMNs reaching into neighboring containers than did small target individuals. Our results also suggest that the hydrophobic membrane successfully prevented free water (and subsequent ¹⁵N) movement within pots.

In another rotated-core target plant experiment, guava (Psidium guajava) tree seedlings were grown in large seedling containers embedded within large pots, and all (including the large pots) were filled with the same relatively nutrient-rich soil mixture. When CMNs were severed by rotation in the absence of neighbors, plant growth significantly diminished to the same size as plants within solid containers, suggesting that rotated plants simply had reduced access to the full soil volume of the large pots (Figure 6). When target plants had any number of neighbors, plant size decreased to similar sizes, and any statistically-detectable effect of severing CMNs disappeared (Figure 6).

In a field experiment using rotated-cores made of PVC pipe, one of us investigated the influence of extraradical mycelium on plant performance in a field experiment with Soapberry (Sapindus saponaria L.) seedlings (Figure 7). Although extraradical mycelium beyond pipes had little effect on plant growth during the thirteen-month experiment, severing it by rotation of pipes reduced foliar N, P and Cu concentrations substantially (by 25% or more).

Figure 1. Experiment setup of containers in intact, severed, or control treatments (A), pots in a target plant experiment (B), or microcosms with a hexagonal (C) or square (D) layout of containers. Dark oval spots on modified containers are an opening into the container covered with a 40 µm nylon mesh for fungal hyphae to penetrate (A). Common mycorrhizal networks remain intact with no rotation of the containers, are severed by rotation, or are prevented from establishing with a solid plastic container (A). In a target plant pot experiment, containers can be placed into a foam bottom that positions them (B). For a microcosm experiment, the bottom can by laid out in a hexagonal array with six equidistant, nearest neighbors for each ‘target’ individual (C), or in a square array with four nearest neighbors and another four, slightly more distant, diagonal neighbors for each ‘target’ (D). Panel B is modified from Weremijewicz et al.¹⁰. Please click here to view a larger version of this figure.

Figure 2. Mean (± SE) aboveground and belowground dry weights (g) of target Andropogon gerardii individuals among common mycorrhizal network treatments. Aboveground dry weights are shown as positive values above the abscissa and belowground dry weights are positive values below the abscissa. Aboveground dry weight bars topped by the same letter do not differ by Tukey’s Honestly Significant Difference post-hoc test at ɑ = 0.05. Belowground dry weights did not differ among treatments and thus, are not topped by letters. This figure is modified from Weremijewicz et al.¹⁰. Please click here to view a larger version of this figure.

Figure 3. Total neighbor (g) versus target plant aboveground dry weight (g) for Andropogon gerardii plants. Plants with intact common mycorrhizal networks (CMNs) are represented by dark triangles and a solid line, with severed CMNs by gray squares and a dashed line, and with no CMNs by white diamonds and a dotted line. This figure is modified from Weremijewicz et al.¹⁰. Please click here to view a larger version of this figure.

Figure 4. Target aboveground dry weights (g) versus foliar manganese concentrations (µg·g^-1) of Andropogon gerardii. Plants with intact common mycorrhizal networks (CMNs) are represented by dark triangles and a solid line, with severed CMNs by gray squares and a dashed line, and with no CMN by white diamonds and a dotted line. This figure is modified from Weremijewicz et al.¹⁰. Please click here to view a larger version of this figure.

Figure 5. δ¹⁵N (‰) ± SE of target Andropogon gerardii individuals (A) with intact common mycorrhizal networks (CMNs; black bars), severed CMNs (gray bars), and no CMN (white bars) and percent nitrogen obtained from neighbor container soil by plants with intact CMNs in ambient sun (triangles) or shade (grey squares) versus target aboveground dry weight (g; B). Bars topped by the same letter in panel A do not differ by Tukey’s Honestly Significant Difference post-hoc test at ɑ = 0.05. These figures are modified from Weremijewicz et al.¹⁰. Please click here to view a larger version of this figure.

Figure 6. Mean (± SE) aboveground and belowground dry weights (g) of target Psidium guajava individuals among common mycorrhizal networks (CMNs) and neighbor treatments. Along the abscissa, a no neighbor treatment is represented by “0N”, one neighbor by “1N,” etc., while a control treatment with no CMNs (inoculated solid container and no neighbors) is represented by light shading and the letter “C”. Biomass of plants with intact CMNs are represented by solid bars, while those with severed CMNs are hachured. Aboveground dry weights are shown as positive values above the abscissa and belowground dry weights are positive values below the abscissa. Bars topped by the same letter do not differ by Tukey’s Honestly Significant Difference post-hoc test at ɑ = 0.05. Aboveground and belowground dry weights of the control treatment were only compared with intact and severed CMN treatments with no neighbors (indicated by Greek letters) because the control did not include neighbors as an additional factor in the treatment. Please click here to view a larger version of this figure.

Figure 7. Extension of the rotated core method to a field experiment (A) and representative 13-month-old Sapindus saponaria L. seedlings with intact (not rotated) and severed (rotated) common mycorrhizal networks (B) . Polyvinyl chloride pipes (9 cm diameter x 20 cm height) were drilled with a hole-saw to have four 5.3 cm diameter holes in two opposed pairs. The holes were covered with a nylon silk-screen mesh with 30 µm pores through which extraradical mycelium could extend both from and into the cores which were filled with soil from the planting site (A). Common mycorrhizal networks were kept intact or severed by rotation using a large pipe-wrench. Positions of paired rotated and non-rotated cores (about 20 cm apart) are marked by flags every 2 m along five transects in the experimental plot located in a Lychee grove (A). Evidence of the disruption of extraradical mycelium reducing N, P and Cu uptake is shown by the chlorotic plants labeled “rotated” shown in B. Please click here to view a larger version of this figure.

Discussion

Our results affirm that our rotated core method can sharply focus on the role of CMNs in belowground plant interactions. There are several critical steps in the protocol, however, that if altered, have potential to influence the ability to detect CMN effects. It is critical to fill the interstitial area surrounding containers with a nutrient-poor medium. In our unsuccessful, rotated-core target plant experiment with guava tree seedlings, although there was a marked reduction of target growth in the presence of any number of neighbors, no effects of CMNs on belowground competition were detected, probably because of mineral nutrient availability throughout the pots. In contrast, the use of a nutrient-poor medium between rotated cores ensures that hyphae must reach into neighboring containers which often are filled with both hyphae and roots (especially when working with root-intensive grasses). Extraradical hyphae in neighboring containers thus are in direct competition with root systems and must partition mineral nutrients acquired from such ‘patches’ among plants connected to a CMN. Another critical component in making belowground interactions detectable is to avoid aboveground competition. Our guava experiment revealed that the effect of additional soil volume access evident when the target plants had no neighbors was essentially eliminated when target seedlings were shaded by neighbors. Using grasses which mostly grow vertically, or constraining seedling leaf crowns to prevent overlap would help to mitigate aboveground interactions.

The use of somewhat rigid containers instead of mesh bags, is critical in maintaining a long experiment with ease of severing CMNs through rotation. In an early attempt at a CMN experiment, trying to pull a knife between mesh bags to sever CMNs not only resulted in damaged bags from which roots could protrude but also seemed to favorably increase soil aeration resulting in dramatically enhanced plant growth when CMNs were severed. Because the rotated core approach gently moves each container in an invariant position (thanks to the supporting position holes at the bottom of the pot or microcosm), it minimizes surrounding substrate disruption and potential aeration. It is absolutely critical, however, to thoroughly water the pots after rotation of containers to return low-fertility, interstitial sand substrate to closely contact the containers.

The proposed rotated core method may be modified in a number of ways to answer a variety of questions regarding the functioning of CMNs and extraradical mycelia. For example, the amount of carbon available for host plants to provide CMNs can be reduced by shading¹⁰. Shade cloth wrapped around modified seedling protectors to encircle individual containers was successful at reducing carbon provisioning to CMNs and thus, ¹⁵N uptake from CMNs¹⁰. Additionally, population structure can be investigated in large microcosms (Figure 1C, D) comprising many plants, each in an individual, rotated container. It is important to note, however, that care must be taken to avoid pseudoreplication⁴¹ when doing so. Individual plants are most certainly not ‘replicates’ because they are not independent of the other plants in a microcosm. Instead, the entire experimental unit (pot or microcosm) is a replicate, which is why we used averaged or totaled neighbor plant sizes per pot prior to running analyses of variance or linear regressions.

Our approach can be modified for field studies to exclude root competition and investigate the influence of intact CMNs. By substituting containers with PVC pipe pieces with large holes covered with nylon silk-screen mesh, rotated cores can withstand harsh field conditions, as in the Soapberry experiment. Similar to our guava pot experiment, however, the effect of severing potential CMNs could not be distinguished from simply restricting the soil volume from which mineral nutrients could be acquired.

Our approach provides a controlled, careful comparison of plants interacting across CMNs versus mycorrhizal plants that are not persistently interconnected (instead of plants entirely lacking mycorrhizas). Hence, it mimics aspects of nature, such as seedlings joining established CMNs as well as the use of a suite of AM fungi. Recent work has demonstrated that different AM fungus species may be different quality partners to plants, and that the presence of a second species of AM fungus on a root system can induce an ‘uncooperative’ fungus species to provide more phosphorus in return for carbon than when alone on the root system⁴². Moreover, different species of fungi may provide benefits other than mineral nutrient acquisition to plant hosts, such as drought and salinity tolerance or protection from pathogens². These findings underscore the importance of using a suite of fungi to establish CMNs. Notwithstanding its realism, a conspicuous limitation of our approach is experiment duration. The size of containers or PVC pipes limits the length of time before plants become root bound, and thus tends to restrict focus to only seedlings or young saplings. Nevertheless, we submit that there is considerable flexibility in the design of target-plant rotated-core experiments in which either or both targets and neighbors can be manipulated in a wide variety of ways to understand the roles of CMNs.

Divulgazioni

The authors have nothing to disclose.

Acknowledgements

We would like to thank the two anonymous reviewers for their suggestions. We also thank the numerous undergraduates who have helped with constructing pots, microcosms, and slotted containers and who have assisted with maintaining and harvesting experiments. We also thank North Central College for startup funds (to JW) and current facilities, as well as Ashley Wojciechowski for obtaining a North Central College Richter Grant supporting an experiment using these methods. Part of this work was funded by a National Science Foundation Doctoral Dissertation Improvement Grant (DEB-1401677).

Materials

Commercial tubular seedlings container (called 'containers' in the manuscript)	Stuewe and Sons, Inc	Ray Leach Cone-tainer ™	RLC3U
Course glass beads	Industrial Supply, Inc.	12/20 sieve	Size #1
Course silica sand	Florida Silica Sand	6/20 50lb bags	None
Fine glass beads	Black Beauty	Black Beauty FINE Crushed Glass Abrasive (50 lbs)	BB-Glass-Fine
Hydrophobic membrane	Gore-tex	None	None
Large commercial tubular seedling containers	Stuewe and Sons, Inc.	Deepot ™	D16L
Medium silica sand	Florida Silica Sand	30/65 50 lb bags	None
Nylon mesh	Tube Lite Company, Inc.	Silk screen	LE7-380-34d PW YEL 60/62 SEFAR LE PECAP POLYESTER
Soil and foliar nutrient analysis facility	Kansas State University Soil Testing Lab	None	None
Stable isotope core facility	University of Miami	None	None

Riferimenti

Remy, W., Taylor, T. N., Hass, H., Kerp, H. Four hundred-million-year-old vesicular arbuscular mycorrhizae. Proceedings of the National Academy of Sciences of the United States of America. 91 (25), 11841-11843 (1994).
Smith, S. E., Read, D. J. . Mycorrhizal Symbiosis. , (2008).
Giovannetti, M., Avio, L., Sbrana, C. . Mycorrhizal Networks. , 41-67 (2015).
Giovannetti, M., Sbrana, C., Cresti, A., Heath, M., Geitmann, I. B. . Cell Biology of Plant and Fungal Tip Growth. Vol. 328. Nato Science Series, Sub-Series I: Life and Behavioural Sciences. , 221-231 (2001).
Giovannetti, M., Sbrana, C., Avio, L., Strani, P. Patterns of below-ground plant interconnections established by means of arbuscular mycorrhizal networks. New Phytologist. 164 (1), 175-181 (2004).
Avio, L., Pellegrino, E., Bonari, E., Giovannetti, M. Functional diversity of arbuscular mycorrhizal fungal isolates in relation to extraradical mycelial networks. New Phytologist. 172 (2), 347-357 (2006).
Giovannetti, M., et al. At the root of the wood wide web: self recognition and nonself incompatibility in mycorrhizal networks. Plant Signaling & Behavior. 1 (1), 1-5 (2006).
Miller, R., Kling, M. J. The importance of integration and scale in the arbuscular mycorrhizal symbiosis. Plant and Soil. 226 (2), 295-309 (2000).
Miller, R., Jastrow, J., Reinhardt, D. R. External hyphal production of vesicular-arbuscular mycorrhizal fungi in pasture and tallgrass prairie communities. Oecologia. 103 (1), 17-23 (1995).
Weremijewicz, J., Sternberg, L. d. S. L. O., Janos, D. P. Common mycorrhizal networks amplify competition by preferential mineral nutrient allocation to large host plants. New Phytologist. , (2016).
Fellbaum, C. R., et al. Fungal nutrient allocation in common mycorrhizal networks is regulated by the carbon source strength of individual host plants. New Phytologist. 203 (2), 646-656 (2014).
Lekberg, Y., Hammer, E. C., Olsson, P. A. Plants as resource islands and storage units–adopting the mycocentric view of arbuscular mycorrhizal networks. FEMS Microbiol Ecol. 74 (2), 336-345 (2010).
Jakobsen, I., Hammer, E. C. . Mycorrhizal Networks. , 91-131 (2015).
Jakobsen, I., Rosendahl, L. Carbon flow into soil and external hyphae from roots of mycorrhizal cucumber plants. New Phytologist. 115 (1), 77-83 (1990).
Kiers, E. T., et al. Reciprocal rewards stabilize cooperation in the mycorrhizal symbiosis. Science. 333 (6044), 880-882 (2011).
Hartnett, D. C., Hetrick, B. A. D., Wilson, G. W. T. Mycorrhizal influence on intra- and interspecific neighbour interactions among co-occuring prairie grasses. Journal of Ecology. 81 (4), 787-795 (1993).
Hetrick, B. A. D., Wilson, G. W. T., Todd, T. C. Differential responses of C3 and C4 grasses to mycorrhizal symbiosis, phosphorus fertilization, and soil microorganisms. Canadian Journal of Botany. 68 (3), 461-467 (1990).
Johnson, D., Leake, J. R., Read, D. J. Novel in-growth core system enables functional studies of grassland mycorrhizal mycelial networks. New Phytologist. 152 (3), 555-562 (2001).
Leake, J. R., et al. Networks of power and influence: the role of mycorrhizal mycelium in controlling plant communities and agroecosystem functioning. Canadian Journal of Botany-Revue Canadienne De Botanique. 82 (8), 1016-1045 (2004).
Babikova, Z., et al. Underground signals carried through common mycelial networks warn neighbouring plants of aphid attack. Ecology Letters. 16 (7), 835-843 (2013).
Schüepp, H., Miller, D. D., Bodmer, M. A new technique for monitoring hyphal growth of vesicular-arbuscular mycorrhizal fungi through soil. Transactions of the British Mycological Society. 89 (4), 429-435 (1987).
Miller, D. D., Bodmer, M., Schüepp, H. Spread of endomycorrhizal colonization and effects on growth of apple seedlings. New Phytologist. 111 (1), 51-59 (1989).
Jakobsen, I., Gazey, C., Abbott, L. K. Phosphate transport by communities of arbuscular mycorrhizal fungi in intact soil cores. New Phytologist. 149 (1), 95-103 (2001).
Johnson, D., Leake, J., Ostle, N., Ineson, P., Read, D. J. In situ 13CO2 pulse‐labelling of upland grassland demonstrates a rapid pathway of carbon flux from arbuscular mycorrhizal mycelia to the soil. New Phytologist. 153 (2), 327-334 (2002).
Johnson, D., Leake, J., Read, D. J. Transfer of recent photosynthate into mycorrhizal mycelium of an upland grassland: short-term respiratory losses and accumulation. of 14C. Soil Biology and Biochemistry. 34 (10), 1521-1524 (2002).
Walder, F., et al. Mycorrhizal networks: Common goods of plants shared under unequal terms of trade. Plant Physiology. 159 (June 2012), 789-797 (2012).
Song, Y. Y., et al. Interplant communication of tomato tlants through underground common mycorrhizal networks. Plos One. 5 (10), e13324 (2010).
Merrild, M. P., Ambus, P., Rosendahl, S., Jakobsen, I. Common arbuscular mycorrhizal networks amplify competition for phosphorus between seedlings and established plants. New Phytologist. 200 (1), 229-240 (2013).
Janos, D. P., Scott, J., Aristizábal, C., Bowman, D. M. J. S. Arbuscular-mycorrhizal networks inhibit Eucalyptus tetrodonta seedlings in rain forest soil microcosms. Plos One. 8 (2), e57716 (2013).
Wyss Lozano Hoyos, T. . Pinus elliottii var. densa Seedling Performance Reflects Ectomycorrhizas, Soil Nutrient Availability and Root Competition. , (2010).
Mäder, P., Vierheilig, H., Alt, M., Wiemken, A. Boundries between soil compartments formed by microporous hydrophobic membranes (GORE-TEX) can be crossed by vesicular-arbuscular mycorrhizal fungi but not by ions in the soil solution. Plant and Soil. 152, 201-206 (1993).
Mäder, P., et al. Transport of 15N from a soil compartment separated by a polytetrafluoroethylene membrane to plant roots via the hyphae of arbuscular mycorrhizal fungi. New Phytologist. 146 (1), 155-161 (2000).
Brundrett, M., Bougher, N., Dell, B., Grove, T. . Working with Mycorrhizas in Forestry and Agriculture. , (1996).
McGonigle, T. P., Miller, M. H., Evans, D. G., Fairchild, G. L., Swan, J. A. A new method which gives an objective-measure of colonization of roots by vesicular arbuscular mycorrhizal fungi. New Phytologist. 115 (3), 495-501 (1990).
Weremijewicz, J., Janos, D. P. Common mycorrhizal networks amplify size inequality in Andropogon gerardii monocultures. New Phytologist. 198 (1), 203-213 (2013).
Weremijewicz, J., O’Reilly, L. d. S. L., Janos, D. P. Arbuscular common mycorrhizal networks mediate intra-and interspecific interactions of two prairie grasses. Mycorrhiza. , 1-13 (2017).
Weiner, J. Asymmetric competition in plant populations. Tree. 5 (11), 360-364 (1990).
Damgaard, C., Weiner, J. Describing inequality in plant size or fecundity. Ecology. 81 (4), 1139-1142 (2000).
Johnson, C. R., Joiner, J. N., Crews, C. E. Effects of N, K, and Mg on growth and leaf nutrient composition of 3 container grown woody ornamentals inoculated with mycorrhizae. Journal of the American Society for Horticultural Science. 105 (2), 286-288 (1980).
Estrada-Luna, A. A., Davies, F. T., Egilla, J. N. Mycorrhizal fungi enhancement of growth and gas exchange of micropropagated guava plantlets (Psidium guajava L.) during ex vitro acclimatization and plant establishment. Mycorrhiza. 10 (1), 1-8 (2000).
Hurlbert, S. H. Pseudoreplication and the design of ecological field experiments. Ecological Monographs. 54 (2), 187-211 (1984).
Argüello, A., et al. Options of partners improve carbon for phosphorus trade in the arbuscular mycorrhizal mutualism. Ecology Letters. 19 (6), 648-656 (2016).

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Weremijewicz, J., Janos, D. P. Investigation of Plant Interactions Across Common Mycorrhizal Networks Using Rotated Cores. J. Vis. Exp. (145), e59338, doi:10.3791/59338 (2019).