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. 2022 Dec 7;9(12):211592. doi: 10.1098/rsos.211592

Spatial scales of competition and a growth–motility trade-off interact to determine bacterial coexistence

Thierry Kuhn 1,2,, Marine Mamin 1,, Saskia Bindschedler 1, Redouan Bshary 2, Aislinn Estoppey 1, Diego Gonzalez 1, Fabio Palmieri 1, Pilar Junier 1,, Xiang-Yi Li Richter 1,2,
PMCID: PMC9727664  PMID: 36483758

Abstract

The coexistence of competing species is a long-lasting puzzle in evolutionary ecology research. Despite abundant experimental evidence showing that the opportunity for coexistence decreases as niche overlap increases between species, bacterial species and strains competing for the same resources are commonly found across diverse spatially heterogeneous habitats. We thus hypothesized that the spatial scale of competition may play a key role in determining bacterial coexistence, and interact with other mechanisms that promote coexistence, including a growth–motility trade-off. To test this hypothesis, we let two Pseudomonas putida strains compete at local and regional scales by inoculating them either in a mixed droplet or in separate droplets in the same Petri dish, respectively. We also created conditions that allow the bacterial strains to disperse across abiotic or fungal hyphae networks. We found that competition at the local scale led to competitive exclusion while regional competition promoted coexistence. When competing in the presence of dispersal networks, the growth–motility trade-off promoted coexistence only when the strains were inoculated in separate droplets. Our results provide a mechanism by which existing laboratory data suggesting competitive exclusion at a local scale is reconciled with the widespread coexistence of competing bacterial strains in complex natural environments with dispersal.

Keywords: bacterial–fungal interactions, growth–motility trade-off, dispersal, coexistence, spatial structure, fungal highway

1. Introduction

Bacteria are important components of the microbial community in diverse habitats, and the coexistence of different bacterial species and strains can serve important ecosystem functions, from soil nutrient cycling to providing defence against pathogens for their animal and plant hosts [15]. Competition experiments under controlled laboratory conditions revealed a general trend that the closer the phylogenetic distance between the competing species, the more likely that one species/strain competitively excludes the other, since niche overlap and antagonistic interactions are generally more intense between closely related species [68]. Nevertheless, competing species with overlapping niche use are commonly observed in natural habitats, including soils [9,10], fermented foods [11,12] and different parts of the human body [1316]. Various mechanisms have been identified to promote the coexistence of bacteria [17], for example, metabolic niche partitioning [1820], negative frequency-dependent selection [2123], shared predators or parasites [24,25] and chemical warfare [2628]. Many of these mechanisms involve trade-offs between growth rate and other traits, such as the production and/or tolerance of antibiotics, resistance to adverse environments and predator avoidance.

One understudied trade-off is the trade-off between bacterial growth and motility. This trade-off can result from the metabolic costs of expressing and using propulsion machinery (e.g. flagella) and genetic constraints that limit the simultaneous improvement of growth and motility during evolution [2934]. The growth–motility trade-off is interesting because it may help explain and reconcile the apparently conflicting results of a strong tendency of competitive exclusion found in laboratory experiments between competing species of overlapping resource niches and the widespread coexistence of intensely competing strains in nature. In contrast with the often spatially simple and well-mixed conditions in competition assays, natural environments such as the soil, skin and fermented foods are featured by spatial heterogeneity that allows bacterial cells to interact at different spatial scales and allows motile strains to disperse. Indeed, studies in animals and plants have shown that the competition–dispersal trade-off (analogous to the growth–motility trade-off in bacteria) can contribute to the coexistence of closely related species at relatively large regional spatial scales, but not at the smaller local scales [35,36]. Recent studies with bacteria also showed that a negative correlation between growth rate and dispersal ability can promote coexistence of closely related Pseudomonas fluorescens [37] strains and Escherichia coli [32] strains. However, the experimental designs in these studies are highly simplified from biological reality. In the former study [37], the dispersal of bacteria was implemented by artificially transferring cell suspension across wells in 96-well plates at discrete time intervals, and in the later work [32], a simple and homogeneous soft agar gel was used as the substrate where bacterial growth and dispersal took place. Therefore, there is need to test the effects of spatial scales of competition and the growth–motility trade-off incorporating other relevant biological factors, for example, in spatially heterogeneous environments created naturally by fungal hyphae networks where bacterial cells have the opportunity to disperse by swimming by means of their flagella.

In this work, we study whether the spatial scale of competition can change the competition outcome between two closely related Pseudomonas putida strains in the presence of a growth–motility trade-off. We created heterogeneous environments by providing biotic and abiotic dispersal networks. The biotic networks were formed by living fungal mycelia [11,38,39], known as ‘fungal highways’, in the soil environment [38]. The abiotic networks were based on glass fibres, which have been used in previous studies as an abiotic control for fungal hyphae [3943]. In the absence of a dispersal network, the two bacterial strains compete either at the local scale when inoculated in mixed cell suspensions, or at the regional scale when inoculated in single-strain suspensions onto the same medium in a Petri dish. In the former case, direct contact between cells of different strains can occur, while in the latter case, cells of different strains do not touch each other but compete by using a shared nutrient pool in the medium or can exchange volatile signals. In the presence of abiotic or biotic dispersal networks, the two bacterial strains compete at intermediate scales that were initially local/regional when inoculated in mixed/separate droplets, respectively. We performed experiments with a factorial design of three different spatial structures (i.e. no dispersal network, abiotic network and biotic network) and two initial scales of competition (i.e. local scale in mixed inoculation and regional scale in separate inoculation), and quantified the competition results in terms of whether the faster growing strain can competitively exclude its slower growing competitor.

2. Materials and methods

2.1. Bacterial and fungal strains

For all experiments, we used two closely related flagellated strains of Pseudomonas putida. The KT2440 strain is a saprotrophic soil bacterium, originally isolated from the rhizosphere [44]; the UWC1 strain is documented as a spontaneous rifampicin-resistant mutant of the KT2440 [45]. A comparison between the genomes of the two strains showed additional differences, with a median identity of 95.8% between homologous genes (see electronic supplementary material, documents ‘genome_comparison.pdf’ and ‘genome_comparison_table.xls'). The KT2440 and UWC1 strains were tagged with the green fluorescent protein (GFP) and mCherry, respectively, by Mini-Tn7 transposon insertions [46,47]. The different fluorescent labels enabled the two strains to be observed by epifluorescence stereomicroscopy and enumerated by flow cytometry. The fungal species used in the experiments was Trichoderma rossicum (NEU388) [43], a saprotrophic soil ascomycete that has been shown to allow various bacterial species (including P. putida) to move along its mycelial networks.

2.2. Culture conditions and inocula preparation

Bacterial cells were cryo-preserved in 30% (v/v) glycerol at −80°C. To prepare the inocula, cells were first plated on Nutrient Agar (NA, 23 g l−1, Carl Roth, AE92.2) supplemented with gentamycin (10 ppm) and grown at 30°C in darkness. The strains were then subcultured once on NA through polygonal spreading and grown under the same conditions. Bacterial suspensions were prepared from overnight cultures grown in Nutrient Broth (NB, 25 g l−1, Carl Roth, AE92.2) at ambient temperature under constant agitation at 120 r.p.m. Bacteria were collected from an overnight culture by centrifugation (3000g for 10 min), washed once and resuspended in 0.01 M phosphate-buffered saline (PBS: 1.5 g l−1 Na2HPO3·2H2O, 0.25 g l−1 NaH2PO3·2H2O, 8.5 g l−1 NaCl and pH adjusted to 7.4). The cell densities of the two bacterial strains in the suspensions were determined by flow cytometry (see below) and then adjusted to the same value of 109 cells ml−1. After that, for the local competition scenario, a 1 : 1 ratio cell suspension was prepared by combining a proportion of the single-strain suspensions.

The fungus T. rossicum was maintained on a slanted agar tube at 4°C. It was plated on the malt-agar medium (MA: 12 g l−1 malt extract Pulver amber, SIOS Homebrewing; 15 g l−1 technical agar, BioLife Italiana) and incubated at 22°C in darkness. Before being used for inoculation, the fungus was subcultured by replating a plug cored from the active apical margin of the 2-day-old mycelial colony on a fresh medium and grown under the same conditions.

2.3. Experimental set-up

As shown in figure 1a, we inoculated the mCherry-labelled UWC1 strain and the GFP-labelled KT2440 strain in droplets of either single-strain or mixed cell suspensions onto plates of MA medium, under three different spatial conditions—no network, fungal mycelial network and glass fibre network—each with four to eight replicates.

Figure 1.

Figure 1.

(a) Diagram of the experimental set-up under spatial settings representing different spatial scales of competition. The inocula are represented in the diagram as disproportionally large for the purpose of a clear illustration. The diameters of the bacteria/PBS inocula and the fungal inocula were 5.8 mm and 5.0 mm, respectively. See (b) for a diagram of the actual positions of different inoculates on a diameter 9 cm Petri dish. When applicable, the fungus or the PBS control was inoculated at position A, the KT2440 strain suspension was inoculated at position B, the mixed inoculum was inoculated at position C, and the UWC1 strain was inoculated at position D.

In the ‘no network’ settings, both bacterial strains have limited capacity to disperse. The colonies (both separate or mixed) can only expand from the colony margin (electronic supplementary material, figure S1). Under the ‘fungal network’ and ‘glass fibre network’ settings, the two bacterial strains used their flagella to swim and thereby dispersed in the liquid film along the surface of fungal hyphae or glass fibres, respectively [39].

In the network settings, when the two bacterial strains were inoculated separately, each strain could grow and start to disperse before encountering each other, and therefore the scale of interaction was initially regional. In this case, although the bacterial cells of the two strains were not in direct contact, they can still compete for resources diffused in the culturing medium in the same Petri dish. When inoculated in mixed droplets, the two strains engaged in direct competition right from the start before they could disperse, and thus the competition was initially local. Overall, the competition between the two strains occurred at finer scales when inoculated in mixed droplets, and the spatial scale of competition was coarser when the two strains were inoculated in separate droplets.

The bacteria and fungi inocula and the PBS control were positioned according to the diagram in figure 1b. The distances between the inocula were determined based on preliminary tests. The relatively shorter distances between point A (where the fungi or PBS control were inoculated) and the other inocula ensure a quick start of bacterial–fungal interactions (the fungal mycelium network can grow past the bacteria inocula within 24 h, see electronic supplementary material, figure S2). The relatively larger distance between inocula B and D ensures that the separate colonies of the KT2440 and UWC1 strains did not get in direct contact by the end of the experiments (electronic supplementary material, figure S3). We kept the positions of inoculation in figure 1b fixed throughout all treatments to ensure that the fungal networks were of the same ‘age’ when they expand and enter into contact with the bacterial colonies, because younger and older mycelia behave differently when interacting with bacterial colonies. Younger mycelial networks tend to stay outside bacterial colonies (electronic supplementary material, figure S4a,b; fungal hyphae tips are in contact with bacterial colonies only at the colony margin) while older mycelial networks expand into the bacterial colonies (electronic supplementary material, figure S4c,d; fungal hyphae tips are accessible to bacterial cells in the interior of the colonies). Because the UWC1 strain tends to constrain the KT2440 strain to the interior of a mixed colony (electronic supplementary material, figure S1c), the KT2440 strain has a better chance to access and disperse on fungal networks (compare electronic supplementary material, figure S5b and S5d; green cells were constrained to the interior of the bacterial colony in the electronic supplementary material, figure S5b, but they were able to spread on the fungal hyphae in the electronic supplementary material, figure S5d).

2.4. Inoculation procedures and culture conditions

In the ‘no network’ setting, the inoculations of bacterial suspensions with separate/mixed strains and the PBS control were carried out by dropping on the medium surface 3 µl of the vortexed suspension with a microsyringe (Hamilton® 1701 N syringe 10 µl needle size 26s ga) according to the corresponding positioning scheme in figure 1. The resulting inocula were round-shaped with an area of 0.27 ± 0.011 cm2.

In the ‘glass fibre network’ setting, we first placed around 30 glass fibres (8 µm diameter, 3–6 cm length, Cole-Parmer, USA) randomly on the agar plate and then performed the inoculations of bacteria as described earlier.

In the ‘fungal networks’ setting, we first inoculated the fungus as a diameter 5 mm plug cored with the wide-end of a Pasteur capillary pipette from the distal part of the T. rossicum mycelial network. Note that the mycelium was not in direct contact with the medium but laid on the top of the plug. The two bacterial strains in separate or mixed droplets were inoculated immediately afterwards according to the schemes in figure 1, following the same procedures as under the ‘no network’. To prevent the fungal inoculum agar plug from impeding the expansion of bacterial colony/colonies, we removed it after 24 h, when the mycelial network had already expanded to the medium surface in the Petri dish.

After inoculation, the plates were parafilmed and incubated, in an upright position, at 22°C in constant darkness.

2.5. Collection of bacterial cells for enumeration

After 5 days of growth, the bacteria cells were collected for enumeration by flow cytometry. Under the ‘no network’ settings, we retrieved all bacterial cells by scraping the whole colony and resuspending the cells in 0.22 µm-filtered PBS. The suspensions were then stored on ice.

Under the ‘glass fibre network’ and the ‘fungal network’ settings, we first removed the bacterial colonies from the plates with a scalpel. We excluded cells in the bacterial colonies because we aimed to examine the relative abundance of the two bacterial strains that had already dispersed in the fungal/glass fibre networks. To collect those cells, we added 7 ml filtered PBS to the Petri dish, closed it and agitated it at 100 r.p.m. for 20 min on a rotary shaker. After that, we intensively flushed the surface of the medium with a 1000 µl micropipette, collected 5 ml of the resulting suspension and stored it on ice.

All the suspensions were then sonicated in a sonic bath at 35 kHz (Transsonic 310, Elma) twice for 30 s each and with a 30 s break in between [38]. This step was done to disaggregate bacterial clumps and/or to separate cells that might have stuck to the fungal/glass fibre fragments that might present in the suspension by chance. To remove those fragments before the flow cytometry analysis, we filtered the suspension through a polycarbonate filter with pores of 10 µm (Whatman, Nucleopore Track-Etch Membrane) pre-autoclaved in the Swinnex filters holders. All samples were kept at 4°C before performing the flow cytometry analysis the day after.

2.6. Flow cytometry

We estimated the relative abundances of the bacterial strains with a CyFlow space cytometer (Partec-System) equipped with a blue laser (480 nm/20 mV) and a green laser (532 nm/30 mV). The forward scatter (FSC) and side scatter (SSC) optical parameters are associated with the blue laser. The green fluorescence of the KT2440 strain was excited by the blue laser and detected on a photomultiplier tube with a 488 nm bandpass filter (FL1 parameter). The red fluorescence of the UWC1 strain was excited by the green laser and detected on a photomultiplier tube associated with a 590/50 nm bandpass filter (FL2 parameter). The lasers were arranged in parallel, with a delay of 50 µs between the two signals. Calibration of the instruments was verified before the analysis with calibration beads (Partec-Sysmex). The leading trigger was set on SSC, with a lower threshold of 500. Gains were set to 700 for FL1 and 750 for FL2. A four-decade logarithmic amplification was used for all parameters. The instrument was equipped with a true volumetric absolute counting facility: events were counted in a defined volume of 200 µl. A speed of 2 µl s−1 was used. We diluted the samples with 0.22 µm-filtered PBS to reach an event rate of approximately 1500 total events s−1. This rate was determined with preliminary assays to yield an optimal signal to noise ratio. Samples were kept on ice during the whole analysis and were run in random order. Analysis of the flow cytometry data was performed with the instrument software FloMax. Events corresponding to the mCherry and GFP fluorescent signals were selected and counted with a quadrant gate set on a biplot of the FL1 and FL2 parameters.

2.7. Data preparation and statistics

We focused on the relative abundance of the UWC1 and KT2440 strains, and therefore, we calculated the cell density ratio in each replicate at the end of the experiments. We then transformed the data by taking the common log (of base 10) and confirmed the normality of the transformed data with the Shapiro–Wilk normality test. We then performed the Student's t-test against our null hypothesis that the relative abundance of the two strains remains identical to that at the beginning of experiments (with a log ratio of zero). The competitions between the abundances of the two strains when inoculated in mixed or separate droplets were performed by the Welch's two-sample t-tests. The statistical significance threshold value was chosen at p = 0.05. We adjusted the p-values to account for the false discovery rate due to multiple comparisons using the Benjamini and Hochberg method [48]. All statistical analyses were carried out within the R statistical environment [49]. The R scripts are provided in the electronic supplementary material, Information.

3. Results

Under the no network’ treatment, when bacteria cells were inoculated in separate droplets (corresponding to regional competition), the relative abundance of the KT2440 strain and the UWC1 strain remained similar (p = 0.569) after 5 days of growth (figure 2a, tables 1 and 2). By contrast, in mixed inocula (corresponding to local competition), the UWC1 strain reached much higher cell proportions (p < 0.01) at the end of the experiments (the UWC1 strain was on average 5.43 times more abundant than the KT2440 strain), showing a growth advantage of the UWC1 strain in direct competition. Moreover, the spatial distribution of the two fluorescently tagged strains indicated that the UWC1 strain has expanded faster and constrained the KT2440 strain to the interior of the mixed colony, thus blocking the further growth of the KT2440 strain (figure 2b). The marked difference in the relative competitiveness of the two strains implies the competitive exclusion of the KT2440 strain by the UWC1 strain at the local scale in the long term.

Figure 2.

Figure 2.

Box-whisker plots representing the distribution of the common logarithm (base 10) of the cell density ratio (KT2440/UWC1) under different experimental settings. The KT2440/UWC1 strain is more abundant than the other strain above/below the red horizontal line at log ratio of 0, respectively. The boxplot centre lines show the median, box limits show upper and lower quartiles, whiskers show 1.5× interquartile range, and each point corresponds to the result of an independent replicate. The red dashed line represents equal cell densities of the two bacterial strains. The numbers of replicates were 6 and 8 under the ‘no network’ setting for the separate and mixed inoculations, respectively. Under all other settings, the numbers of replicates were 4. Competitive exclusion of the KT2440 strain by the UWC1 strain occurred in two replicates under the fungal network treatment with mixed strain inoculates (the log density ratio was −∞, marked with the two red dots). (b) Colony formed by bacterial strains in a mixed droplet 2 days after inoculation in the absence of a dispersal network. (c) Colony formed by bacterial strains in a mixed droplet in the presence of fungal hyphae networks 2 days after inoculation. Only the UWC1 strain with red fluorescence was visible along the fungal hyphae. (d) Dispersed KT2440 cells along fungal hyphae networks 3 days after being inoculated in a separate droplet. (e) Dispersed UWC1 cells along fungal hyphae networks 2 days after being inoculated in a separate droplet. The pictures were taken at magnifications of 10×, 3×, 5× and 5× with epifluorescence stereomicroscopy in (be), respectively.

Table 1.

The median of the absolute density ratio (before log transformation) of the KT2440 strain relative to the UWC1 strain.

no network glass fibre network fungal network
separate inoculation 1.064 1.239 1.418
mixed inoculation 0.184 0.143 N.A.a

aThe KT2440 strain was competitively excluded in two of the four replicates.

Table 2.

Mean and s.d. of the log density ratio between the KT2440 and the UWC1 strain, and the p-value of the t-test with a null hypothesis that the mean of the log ratio was not significantly different from zero.

no network glass fibre network fungal network
separate inoculation mean ± s.d. 0.030 ± 0.094 −0.006 ± 0.688 0.170 ± 0.111
p-value 0.569 0.978 0.028
mixed inoculation mean ± s.d. −0.746 ± 0.039 −0.820 ± 0.488 N.A.a
p-value <0.01 0.028

aThe KT2440 strain was competitively excluded in two of the four replicates.

Under the ‘glass fibres’ treatment, the KT2440 strain was slightly more abundant (but the difference was not statistically significant, p = 0.978) when the two bacterial strains were inoculated separately (corresponding to an intermediate scale of competition that was initially regional, figure 2a, table 1), reaching 1.239 times the density of the UWC1 strain. We therefore cannot reject the null hypothesis that the relative abundance of the two strains remained identical (table 2). This result implies possible long-term coexistence of the two strains at the regional scale. In plates where the two bacterial strains were inoculated in mixed droplets (corresponding to an intermediate scale of competition that was initially local), similar to the results of local competition under the no network’ treatment, the UWC1 strain has a substantial competitive advantage (p = 0.028) and reached on average 6.99 times the density of the KT2440 strain, implying that competitive exclusion was likely at the local scale (figure 2a, tables 1 and 2).

Under the fungal network’ treatment, the KT2440 strain reached even larger (statistically significant, p = 0.028) relative abundances when inoculated in separate droplets (1.42 times the abundance of the UWC1 strain), implying a competitive advantage at the regional scale. The competitive advantage of the KT2440 strain outside the initial inocula resulted from its higher motility and faster spread in the presence of fungal hyphae networks. See electronic supplementary material, figure S7 for direct verification of the motility advantage of the KT2440 strain. The distribution of bacterial cells in the fungal network can be considered as mini-colonies with either mixed or separate strains. Since the KT2440 strain grows equally fast as the UWC1 strain in separate colonies, and it grows much slower than the UWC1 strain in mixed colonies, the overall higher densities of the KT2440 strain were likely to result from its superior motility in the presence of dispersal networks provided by fungal hyphae. In mixed inoculations, however, the KT2440 strain was competitively excluded outside the initial inocula (figure 2c for an example) in two of the replicates (in these cases, the cell densities of the KT2440 strain were so low that they were not distinguishable from the noise background in the flow cytometry assays), and in the other two replicates, the cell densities of the UWC1 strain were 3.72 times and 10.67 times more abundant than the KT2440 strain (figure 2a, tables 1 and 2). The spatial distribution of the two tagged strains indicated that when inoculated in mixed droplets in the presence of fungal networks, the slower growing KT2440 strain was constrained to the interior of the mixed colony and consequently was not able to disperse through the fungal networks (figure 2c; note that only red fluorescence was visible along the fungal hyphae connected to the colony). By contrast, when inoculated in separate droplets, both bacterial strains can efficiently disperse along fungal hyphae networks (figure 2d,e).

Across all spatial settings, the relative abundance of UWC1 and KT2440 strains differ greatly depending on whether they were inoculated in separate or mixed droplets (figure 2a, table 3), showing the importance of the spatial scale of competition in determining the competition outcome and long-term coexistence of the two bacterial strains, in the presence or absence of dispersal networks.

Table 3.

Comparison between the distributions of the common logarithm (base 10) of the cell density ratio (KT2440/UWC1) under separate and mixed inoculation treatments.

spatial settings p-value of the Welch's two sample t-test
no network <0.001
glass fibre network 0.025
fungal hyphae network N.A., because of the two − ∞ values under mixed inoculation treatment

4. Discussion

Our experimental results showed a clear pattern: local competition between the two bacterial strains (treatments with mixed inocula) caused competitive exclusion, while competition at the regional scale (treatments with separate inocula) is more favourable for coexistence. This is consistent with the effect of the spatial scale on the competition outcome found in larger organisms [35,36]. Our results thus help to reconcile the conflicting findings that bacteria [68] and protists [50] species/strains that overlap in their niches of resource utilization tend to competitively exclude each other in well-mixed liquid cultures (implying local competition), and the widespread phenomenon of microbial species/strains coexisting while competing for the same resources in spatially complex environment (implying regional competition), such as cheese rind [11,12], the human gut [13,16] and skin [14]. It is important to note that spatial complexity does not automatically promote biodiversity. The effect of spatial structure crucially depends on the type of interactions between species, and in some cases, adding spatial structure can lead to the breakdown of diversity and competitive exclusion of species that could have coexisted under a well-mixed environment [5153].

In the current work, we showed that when the competing species are involved in a growth–motility trade-off, spatial structure provided by dispersal networks can help the competing species to coexist. In the presence of dispersal networks, the higher motility of the slower growing strain (KT2440) can confer an advantage only when the initial scale of competition was regional (the two strains were inoculated in separate droplets). Otherwise, the faster growing strain (UWC1) can quickly outgrow the slower growing strain, constraining the latter to the interior of the mixed colony and thus preventing it from dispersing. Instead of comparing the growth rates of the UWC1 and KT2440 strains in isolation, we inferred the growth advantage of the UWC1 strain in direct competition by comparing the log ratios of the cell densities under mixed and separate inoculations in the ‘no network’ setting, controlling that spatial arrangement was the only difference. Microbial growth rates are highly context dependent. Literature has shown that even when growing in monoculture the relative growth rates of competing species can switch in different environments (e.g. in vivo in the host environment and in vitro when cultured in microcosms [54]), and the relative growth rates in co-culture can show complex nonlinear patterns with multiple crossings at different initial frequency combinations [22]. Not only the growth rate, the motility of microorganisms is also context dependent and can be sensitive to environmental conditions [55]. Because of the strong association between microbial growth and dispersal rates and their sensitivity to biotic and abiotic environmental factors, it is important to measure them in the same competition context, as we did in the current work.

Note that the significantly higher abundance of the KT2440 strain in the presence of fungal networks when inoculated in separate droplets does not imply that it can competitively exclude the UWC1 strain for three reasons. First, due to the limitations of the experimental system (e.g. the fungal network has already covered the entire Petri dish and could not expand further by the end of 5 days), our results only showed a snapshot of the competition dynamics and therefore have limited power to predict the entire competition trajectory. In addition, we focused on quantifying the relative abundance of cells outside the colonies formed by the initial inocula, and thus the result of a higher abundance of the KT2440 cells was limited to cells descended from the dispersed ones, and it is possible that the UWC1 strain has nevertheless reached higher abundance inside the initial colony. Finally, our results have shown a consistent growth advantage of the UWC1 strain when competition occurs locally. Therefore, we expect that as soon as the cells of the two strains meet in the dispersal network and engage in direct local competition, the UWC1 strain would overgrow its competitor locally. The competitive advantage of the UWC1 strain in local competition is highly contingent on its ability to block the KT2440 strain from accessing the dispersal network. Unlike diffusible nutrients, space is a non-sharable resource. By occupying specific locations in space, such as the expansion frontiers of a mixed bacterial colony or the locations where a mixed colony meets a dispersal network, the faster growing species (the UWC1 strain in our case) not only prevents its competitor from occupying the same space per se, but also deprives it of the opportunity to use a section of space extending from the colony margin [5658], and in the presence of a dispersal network, also the section of space in the network that is accessible through that location. Existing work has shown that physical interactions play essential roles in shaping the structure of microbial colonies and biofilms [5961]. In this work, we showed that the spatial occupation of the UWC1 cells at the ‘entrance points’ of a dispersal network gives them an ‘opportunity advantage’ to explore and expand to new territories.

The competitive advantage of the KT2440 strain when dispersal is allowed suggests that the growth–motility trade-off plays a role in promoting the coexistence of the two bacterial strains, with the UWC1 strain growing faster under direct competition while the KT2440 is better at dispersing and exploring empty habitats. When competing species are regulated by a trade-off between their rate of reproduction and their ability to disperse, theory predicts that there are conditions where coexistence is possible [62,63]. A previous study with two P. fluorescens strains also demonstrated that regional competition in the presence of a growth–dispersal trade-off can promote coexistence [37]. In the aforementioned study, however, dispersal occurred by manually transferring bacterial cells at discrete intervals. Such experimental design, while promoting the controllability of the system and helping to reduce variation between different replicates, is highly artificial and corresponds to natural conditions that only rarely occur (e.g. occasional heavy rains that saturate the soil for a short time [47,64,65]). In this work, we allowed continuous dispersal of the two bacterial strains, either through glass fibre networks, or fungal mycelial networks that can interact dynamically with the bacteria [66,67]. The bacterial dispersal in our experiments thus corresponds to that in environments such as the typical well-drained soil, where the movement of bacteria is restricted by the thinness and patchiness of the liquid films [68] on the surface of abiotic (e.g. rocks and soil particles) and biotic (e.g. roots and fungal hyphae) components. Despite the additional factors and variation involved, our results showed robustly that interactions at the local scale tend to cause competitive exclusion, while coexistence is more likely when competition is regional.

In this work, the abiotic network was formed by placing thin glass fibres randomly on a Petri dish, while the biotic network was formed by the actively growing fungal hyphae, which follow species-specific structural patterns. The glass fibre network was designed as an abiotic ‘control’ of the fungal network as in several previous studies [3943]. However, our work showed that the glass fibre network is not an ideal abiotic substitute for the fungal network, partly because the liquid films formed around glass fibres are much thicker than those surrounding fungal hyphae (electronic supplementary material, figure S6). The thickness of liquid film determines whether cells can disperse solely actively by flagella-propelled swimming or also passively driven by hydraulic flow in the liquid film [69]. The hydraulic flow caused by inoculation may have flushed some KT2440 cells into the dispersal network, leading to a large variation in the competition outcome under the glass fibre treatment. Another factor contributing to the variation could be the randomness of dispersal network created when placing the extremely thin (8 µm in diameter) and brittle glass fibres on the Petri dish (electronic supplementary material, figure S6). Theory and experiments have shown that the network structure and connectivity can shape biodiversity patterns [70,71]. Since we were not able to precisely control the abiotic network structures in the current work, large variations persist in the relative abundance of the two bacterial strains. This also limits our ability to investigate deeper the interactions between network type and different ways of inoculation, for example, by performing a two-factor ANOVA test. Therefore, a valuable next step would be to tease apart the large variations of our current results under the abiotic and biotic network settings by manipulating their structures, for example, by using three-dimensional printed abiotic hyphae models with fixed structure and surface physico-chemical properties, or microfluidic platforms that constrain the growth of fungal hyphae networks into predefined topology [72,73].

5. Conclusion

To conclude, using experiments with two closely related strains of the bacteria Pseudomonas putida, we found that spatial scales of competition and the growth–motility trade-off interact to determine the competition outcome. We showed that local competition caused competitive exclusion while regional competition is more favourable for coexistence. The results are consistent with previous findings in animals and plants. Furthermore, we showed that in the presence of dispersal networks, the growth–motility trade-off can promote coexistence only when the scale of competition was regional initially. Only in this case, the slower growing but faster dispersing strain has the opportunity to use the dispersal networks to escape from direct local competition with its faster growing competitor. It is interesting to ask whether the phenomenon we observed in this study may generalize to microbial competition dynamics in other spatially complex environments, where interactions occur at different spatial scales and in the presence of dispersal networks provided by diverse fungi and fungi-like organisms. Therefore, we encourage future work to systematically study the interactions between spatial scales of competition and the growth–motility trade-off between pairs of microorganisms with different phylogenetic relatedness. The current work identified new factors that affect microbial competition dynamics in spatially complex environments––in particular, along dispersal networks provided by fungal hyphae, and raised new questions regarding the roles of network topology and the biotic interactions between fungi and different bacterial strains that disperse along them. Future investigations along these lines would help us delve deeper into the mechanisms that govern microbial competition dynamics and coexistence in spatially complex environments.

Acknowledgements

The authors would like to thank Arnaud Dechesne and Jan van der Meer for providing the two bacteria strains. We also thank the associate editor Nicole Hynson and the three anonymous reviewers for their constructive comments and suggestions.

Contributor Information

Pilar Junier, Email: pilar.junier@unine.ch.

Xiang-Yi Li Richter, Email: li@evolbio.mpg.de.

Data accessibility

All data supporting the reported results can be found in the data tables in the manuscript and the electronic supplementary materials [74].

Authors' contributions

T.K.: data curation, formal analysis, investigation, methodology and visualization; M.M.: data curation, formal analysis, investigation, methodology and visualization; S.B.: conceptualization and writing—review and editing; R.B.: conceptualization and writing—review and editing; A.E.: methodology and writing—review and editing; D.G.: conceptualization, supervision and writing—review and editing; F.P.: methodology and writing—review and editing; P.J.: conceptualization, funding acquisition, supervision and writing—review and editing; X.-Y.L.R.: conceptualization, funding acquisition, project administration, supervision, writing—original draft and writing—review and editing.

All authors gave final approval for publication and agreed to be held accountable for the work performed therein.

Conflict of interest declaration

We have no competing interests.

Funding

This research was funded by a U.S. Department of Energy Biological and Environmental Research Science Focus Area grant to P.J. (grant no. DE-AC52-06NA25396) and a Swiss National Science Foundation Ambizione grant to X.-Y.L.R. (grant no. PZ00P3_180145).

References

  • 1.Van Der Heijden MGA, Bardgett RD, Van Straalen NM. 2008. The unseen majority: soil microbes as drivers of plant diversity and productivity in terrestrial ecosystems. Ecol. Lett. 11, 296-310. ( 10.1111/j.1461-0248.2007.01139.x) [DOI] [PubMed] [Google Scholar]
  • 2.Awasthi A, Singh M, Soni SK, Singh R, Kalra A. 2014. Biodiversity acts as insurance of productivity of bacterial communities under abiotic perturbations. ISME J. 8, 2445-2452. ( 10.1038/ismej.2014.91) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 3.Vandenkoornhuyse P, Quaiser A, Duhamel M, Le Van A, Dufresne A. 2015. The importance of the microbiome of the plant holobiont. New Phytol. 206, 1196-1206. ( 10.1111/nph.13312) [DOI] [PubMed] [Google Scholar]
  • 4.Lozupone CA, Stombaugh JI, Gordon JI, Jansson JK, Knight R. 2012. Diversity, stability and resilience of the human gut microbiota. Nature 489, 220-230. ( 10.1038/nature11550) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 5.Rosshart SP, et al. 2017. Wild mouse gut microbiota promotes host fitness and improves disease resistance. Cell 171, 1015-1028. ( 10.1016/j.cell.2017.09.016) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 6.Tan J, Pu Z, Ryberg WA, Jiang L. 2015. Resident-invader phylogenetic relatedness, not resident phylogenetic diversity, controls community invasibility. Am. Nat. 186, 59-71. ( 10.1086/681584) [DOI] [PubMed] [Google Scholar]
  • 7.Jiang L, Tan J, Pu Z. 2010. An experimental test of Darwin's naturalization hypothesis. Am. Nat. 175, 415-423. ( 10.1086/650720) [DOI] [PubMed] [Google Scholar]
  • 8.Russel J, Røder HL, Madsen JS, Burmølle M, Sørensen SJ. 2017. Antagonism correlates with metabolic similarity in diverse bacteria. Proc. Natl Acad. Sci. USA 114, 10 684-10 688. ( 10.1073/pnas.1706016114) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 9.Goberna M, Montesinos-Navarro A, Valiente-Banuet A, Colin Y, Gómez-Fernández A, Donat S, Navarro-Cano JA, Verdú M. 2019. Incorporating phylogenetic metrics to microbial co-occurrence networks based on amplicon sequences to discern community assembly processes. Mol. Ecol. Res. 9, 1552-1564. ( 10.1111/1755-0998.13079) [DOI] [PubMed] [Google Scholar]
  • 10.Lentendu G, Dunthorn M. 2021. Phylogenetic relatedness drives protist assembly in marine and terrestrial environments. Glob. Ecol. Biogeogr. 30, 1532-1544. ( 10.1111/geb.13317) [DOI] [Google Scholar]
  • 11.Zhang Y, Kastman EK, Guasto JS, Wolfe BE. 2018. Fungal networks shape dynamics of bacterial dispersal and community assembly in cheese rind microbiomes. Nat. Commun. 9, 336. ( 10.1038/s41467-017-02522-z) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 12.Kastman EK, Kamelamela N, Norville JW, Cosetta CM, Dutton RJ, Wolfe BE. 2016. Biotic interactions shape the ecological distributions of Staphylococcus species. MBio 7, e01157-16. ( 10.1128/mBio.01157-16) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 13.Li SS, et al. 2016. Durable coexistence of donor and recipient strains after fecal microbiota transplantation. Science (1979) 352, 586-589. [DOI] [PubMed] [Google Scholar]
  • 14.Oh J, Byrd AL, Deming C, Conlan S, Kong HH, Segre JA. 2014. Biogeography and individuality shape function in the human skin metagenome. Nature 514, 59-64. ( 10.1038/nature13786) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 15.Kreth J, Merritt J, Shi W, Qi F. 2005. Competition and coexistence between Streptococcus mutans and Streptococcus sanguinis in the dental biofilm. J. Bacteriol. 187, 7193-7203. ( 10.1128/JB.187.21.7193-7203.2005) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 16.Darcy JL, Washburne AD, Robeson MS, Prest T, Schmidt SK, Lozupone CA. 2020. A phylogenetic model for the recruitment of species into microbial communities and application to studies of the human microbiome. ISME J. 14, 1359-1368. ( 10.1038/s41396-020-0613-7) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 17.Hibbing ME, Fuqua C, Parsek MR, Peterson SB. 2010. Bacterial competition: surviving and thriving in the microbial jungle. Nat. Rev. Microbiol. 8, 15-25. ( 10.1038/nrmicro2259) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 18.Wilson M, Lindow SE. 1994. Coexistence among epiphytic bacterial populations mediated through nutritional resource partitioning. Appl. Environ. Microbiol. 60, 4468. ( 10.1128/aem.60.12.4468-4477.1994) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 19.Song W, Kim M, Tripathi BM, Kim H, Adams JM. 2016. Predictable communities of soil bacteria in relation to nutrient concentration and successional stage in a laboratory culture experiment. Environ. Microbiol. 18, 1740-1753. ( 10.1111/1462-2920.12879) [DOI] [PubMed] [Google Scholar]
  • 20.Nuccio EE, et al. 2020. Niche differentiation is spatially and temporally regulated in the rhizosphere. ISME J. 14, 999-1014. ( 10.1038/s41396-019-0582-x) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 21.Kerr B, Riley MA, Feldman MW, Bohannan BJM. 2002. Local dispersal promotes biodiversity in a real-life game of rock–paper–scissors. Nature 418, 171-174. ( 10.1038/nature00823) [DOI] [PubMed] [Google Scholar]
  • 22.Li XY, Pietschke C, Fraune S, Altrock PM, Bosch TCG, Traulsen A. 2015. Which games are growing bacterial populations playing? J. R. Soc. Interface 12, 20150121. ( 10.1098/rsif.2015.0121) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 23.Harmand N, Federico V, Hindré T, Lenormand T. 2019. Nonlinear frequency-dependent selection promotes long-term coexistence between bacteria species. Ecol. Lett. 22, 1192-1202. [DOI] [PubMed] [Google Scholar]
  • 24.Hiltunen T, Kaitala V, Laakso J, Becks L. 2017. Evolutionary contribution to coexistence of competitors in microbial food webs. Proc. R. Soc. B 284, 20170415. ( 10.1098/rspb.2017.0415) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 25.Li XY, Lachnit T, Fraune S, Bosch TCG, Traulsen A, Sieber M. 2017. Temperate phages as self-replicating weapons in bacterial competition. J. R. Soc. Interface 14, 20170563. ( 10.1098/rsif.2017.0563) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 26.Brown SP, Fredrik Inglis R, Taddei F. 2009. SYNTHESIS: evolutionary ecology of microbial wars: within-host competition and (incidental) virulence. Evol. Appl. 2, 32-39. ( 10.1111/j.1752-4571.2008.00059.x) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 27.García-Bayona L, Comstock LE. 2018. Bacterial antagonism in host-associated microbial communities. Science (1979) 361, eaat2456. [DOI] [PubMed] [Google Scholar]
  • 28.Granato ET, Meiller-Legrand TA, Foster KR. 2019. The evolution and ecology of bacterial warfare. Curr. Biol. 29, R521-R537. ( 10.1016/j.cub.2019.04.024) [DOI] [PubMed] [Google Scholar]
  • 29.Yi X, Dean AM. 2016. Phenotypic plasticity as an adaptation to a functional trade-off. Elife 5, e19307. ( 10.7554/eLife.19307) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 30.Ni B, Ghosh B, Paldy FS, Colin R, Heimerl T, Sourjik V. 2017. Evolutionary remodeling of bacterial motility checkpoint control. Cell Rep. 18, 866-877. ( 10.1016/j.celrep.2016.12.088) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 31.Fraebel DT, Mickalide H, Schnitkey D, Merritt J, Kuhlman TE, Kuehn S. 2017. Environment determines evolutionary trajectory in a constrained phenotypic space. Elife 6, e24669. ( 10.7554/eLife.24669) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 32.Gude S, Pinçe E, Taute KM, Seinen AB, Shimizu TS, Tans SJ. 2020. Bacterial coexistence driven by motility and spatial competition. Nature 578, 588-592. ( 10.1038/s41586-020-2033-2) [DOI] [PubMed] [Google Scholar]
  • 33.Nadell CD, Bassler BL. 2011. A fitness trade-off between local competition and dispersal in Vibrio cholerae biofilms. Proc. Natl Acad. Sci. USA 108, 14 181-14 185. ( 10.1073/pnas.1111147108) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 34.Yawata Y, Cordero OX, Menolascina F, Hehemann JH, Polz MF, Stocker R. 2014. Competition-dispersal tradeoff ecologically differentiates recently speciated marine bacterioplankton populations. Proc. Natl Acad. Sci. USA 111, 5622-5627. ( 10.1073/pnas.1318943111) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 35.Ma C, Li S, Pu Z, Tan J, Liu M, Zhou J, Li H, Jiang L. 2016. Different effects of invader-native phylogenetic relatedness on invasion success and impact: a meta-analysis of Darwin's naturalization hypothesis. Proc. R. Soc. B 283, 20160663. ( 10.1098/rspb.2016.0663) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 36.Park DS, Feng X, Maitner BS, Ernst KC, Enquist BJ. 2020. Darwin's naturalization conundrum can be explained by spatial scale. Proc. Natl Acad. Sci. USA 117, 10 904-10 910. ( 10.1073/pnas.1918100117) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 37.Livingston G, Matias M, Calcagno V, Barbera C, Combe M, Leibold MA, Mouquet N. 2012. Competition-colonization dynamics in experimental bacterial metacommunities. Nat. Commun. 3, 1234. ( 10.1038/ncomms2239) [DOI] [PubMed] [Google Scholar]
  • 38.Kohlmeier S, Smits THM, Ford RM, Keel C, Harms H, Wick LY. 2005. Taking the fungal highway: mobilization of pollutant-degrading bacteria by fungi. Environ. Sci. Technol. 39, 4640-4646. ( 10.1021/es047979z) [DOI] [PubMed] [Google Scholar]
  • 39.Pion M, Bshary R, Bindschedler S, Filippidou S, Wick LY, Job D, Junier P. 2013. Gains of bacterial flagellar motility in a fungal world. Appl. Environ. Microbiol. 79, 6862-6867. ( 10.1128/AEM.01393-13) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 40.Schamfuß S, Neu TR, van der Meer JR, Tecon R, Harms H, Wick LY. 2013. Impact of mycelia on the accessibility of fluorene to PAH-degrading bacteria. Environ. Sci. Technol. 47, 6908-6915. ( 10.1021/es304378d) [DOI] [PubMed] [Google Scholar]
  • 41.Otto S, Banitz T, Thullner M, Harms H, Wick LY. 2016. Effects of facilitated bacterial dispersal on the degradation and emission of a desorbing contaminant. Environ. Sci. Technol. 50, 6320-6326. ( 10.1021/acs.est.6b00567) [DOI] [PubMed] [Google Scholar]
  • 42.Worrich A, et al. 2016. Bacterial dispersal promotes biodegradation in heterogeneous systems exposed to osmotic stress. Front. Microbiol. 7, 1214. ( 10.3389/fmicb.2016.01214) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 43.Bravo D, Cailleau G, Bindschedler S, Simon A, Job D, Verrecchia E, Junier P. 2013. Isolation of oxalotrophic bacteria able to disperse on fungal mycelium. FEMS Microbiol. Lett. 348, 157-166. ( 10.1111/1574-6968.12287) [DOI] [PubMed] [Google Scholar]
  • 44.Regenhardt D, Heuer H, Heim S, Fernandez DU, Strömpl C, Moore ERB, Timmis KN. 2002. Pedigree and taxonomic credentials of Pseudomonas putida strain KT2440. Environ. Microbiol. 4, 912-915. ( 10.1046/j.1462-2920.2002.00368.x) [DOI] [PubMed] [Google Scholar]
  • 45.McClure NC, Weightman AJ, Fry JC. 1989. Survival of Pseudomonas putida UWC1 containing cloned catabolic genes in a model activated-sludge unit. Appl. Environ. Microbiol. 55, 2627-2634. ( 10.1128/aem.55.10.2627-2634.1989) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 46.Rochat L, Péchy-Tarr M, Baehler E, Maurhofer M, Keel C. 2010. Combination of fluorescent reporters for simultaneous monitoring of root colonization and antifungal gene expression by a biocontrol pseudomonad on cereals with flow cytometry. Mol. Plant Microbe Interact. 23, 949-961. ( 10.1094/MPMI-23-7-0949) [DOI] [PubMed] [Google Scholar]
  • 47.Dechesne A, Wang G, Gülez G, Or D, Smets BF. 2010. Hydration-controlled bacterial motility and dispersal on surfaces. Proc. Natl Acad. Sci. USA 107, 14 369-14 372. ( 10.1073/pnas.1008392107) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 48.Benjamini Y, Hochberg Y. 1995. Controlling the false discovery rate: a practical and powerful approach to multiple testing. J. R. Stat. Soc. 57, 289-300. ( 10.1111/j.2517-6161.1995.tb02031.x) [DOI] [Google Scholar]
  • 49.R Core Team. 2021. R: a language and environment for statistical computing. Vienna, Austria: R Foundation for Statistical Computing. See https://www.R-project.org/. [Google Scholar]
  • 50.Violle C, Nemergut DR, Pu Z, Jiang L. 2011. Phylogenetic limiting similarity and competitive exclusion. Ecol. Lett. 14, 782-787. ( 10.1111/j.1461-0248.2011.01644.x) [DOI] [PubMed] [Google Scholar]
  • 51.Saxer G, Doebeli M, Travisano M. 2009. Spatial structure leads to ecological breakdown and loss of diversity. Proc. R. Soc. B 276, 2065-2070. ( 10.1098/rspb.2008.1827) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 52.Weiner BG, Posfai A, Wingreen NS. 2019. Spatial ecology of territorial populations. Proc. Natl Acad. Sci. USA 116, 17 874-17 879. ( 10.1073/pnas.1911570116) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 53.Lowery NV, Ursell T. 2019. Structured environments fundamentally alter dynamics and stability of ecological communities. Proc. Natl Acad. Sci. USA 116, 379-388. ( 10.1073/pnas.1811887116) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 54.Deines P, Hammerschmidt K, Bosch TCG. 2020. Microbial species coexistence depends on the host environment. MBio 11, e00807-20. ( 10.1128/mBio.00807-20) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 55.Ni B, Colin R, Link H, Endres RG, Sourjik V. 2020. Growth-rate dependent resource investment in bacterial motile behavior quantitatively follows potential benefit of chemotaxis. Proc. Natl Acad. Sci. USA 117, 595-601. ( 10.1073/pnas.1910849117) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 56.Hallatschek O, Hersen P, Ramanathan S, Nelson DR. 2007. Genetic drift at expanding frontiers promotes gene segregation. Proc. Natl Acad. Sci. USA 104, 19 926-19 930. ( 10.1073/pnas.0710150104) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 57.Hallatschek O, Nelson DR. 2010. Life at the front of an expanding population. Evolution (N Y) 64, 193-206. [DOI] [PubMed] [Google Scholar]
  • 58.Farrell FD, Gralka M, Hallatschek O, Waclaw B. 2017. Mechanical interactions in bacterial colonies and the surfing probability of beneficial mutations. J. R. Soc. Interface 4, 20170073. ( 10.1098/rsif.2017.0073) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 59.Doumic M, Hecht S, Peurichard D. 2020. A purely mechanical model with asymmetric features for early morphogenesis of rod-shaped bacteria micro-colony. Math. Biosci. Eng. 17, 6873-6908. ( 10.3934/mbe.2020356) [DOI] [PubMed] [Google Scholar]
  • 60.Maier B. 2021. How physical interactions shape bacterial biofilms. Annu. Rev. Biophys. 50, 401-417. ( 10.1146/annurev-biophys-062920-063646) [DOI] [PubMed] [Google Scholar]
  • 61.Warren MR, Sun H, Yan Y, Cremer J, Li B, Hwa T. 2019. Spatiotemporal establishment of dense bacterial colonies growing on hard agar. Elife 8, e41093. ( 10.7554/eLife.41093) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 62.Levins R, Culver D. 1971. Regional coexistence of species and competition between rare species. Proc. Natl Acad. Sci. USA 68, 1246-1248. ( 10.1073/pnas.68.6.1246) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 63.Yu DW, Wilson HB. 2001. The competition-colonization trade-off is dead; long live the competition-colonization trade-off. Am. Nat. 158, 49-63. ( 10.1086/320865) [DOI] [PubMed] [Google Scholar]
  • 64.Št'ovíček A, Azatyan A, Soares MIM, Gillor O. 2017. The impact of hydration and temperature on bacterial diversity in arid soil mesocosms. Front. Microbiol. 8, 1078. ( 10.3389/fmicb.2017.01078) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 65.Št'ovíček A, Kim M, Or D, Gillor O. 2017. Microbial community response to hydration-desiccation cycles in desert soil. Sci. Rep. 7, 45735. ( 10.1038/srep45735) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 66.Deveau A, et al. 2018. Bacterial–fungal interactions: ecology, mechanisms and challenges. FEMS Microbiol. Rev. 42, 335-352. ( 10.1093/femsre/fuy008) [DOI] [PubMed] [Google Scholar]
  • 67.Pion M, Spangenberg JE, Simon A, Bindschedler S, Flury C, Chatelain A, Bshary R, Job D, Junier P. 2013. Bacterial farming by the fungus Morchella crassipes. Proc. R. Soc. B 280, 20132242. ( 10.1098/rspb.2013.2242) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 68.Or D, Smets BF, Wraith JM, Dechesne A, Friedman SP. 2007. Physical constraints affecting bacterial habitats and activity in unsaturated porous media – a review. Adv. Water Res. 30, 1505-1527. ( 10.1016/j.advwatres.2006.05.025) [DOI] [Google Scholar]
  • 69.Kuhn T, Buffi M, Bindschedler S, Chain P, Gonzalez D, Stanley C, Wick L, Junier P, Richter XYL. 2022. Design and construction of 3D printed devices to investigate active and passive bacterial dispersal on hydrated surfaces. BMC Biol. 20, 203. ( 10.1186/s12915-022-01406-z) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 70.Altermatt F, Fronhofer EA. 2018. Dispersal in dendritic networks: ecological consequences on the spatial distribution of population densities. Freshw. Biol. 63, 22-32. ( 10.1111/fwb.12951) [DOI] [Google Scholar]
  • 71.Carrara F, Altermatt F, Rodriguez-Iturbe I, Rinaldo A. 2012. Dendritic connectivity controls biodiversity patterns in experimental metacommunities. Proc. Natl Acad. Sci. USA 109, 5761-5766. ( 10.1073/pnas.1119651109) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 72.Aleklett K, Ohlsson P, Bengtsson M, Hammer EC. 2021. Fungal foraging behaviour and hyphal space exploration in micro-structured Soil Chips. ISME J. 15, 1782-1793.( 10.1038/s41396-020-00886-7) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 73.Gimeno A, et al. 2021. A versatile microfluidic platform measures hyphal interactions between Fusarium graminearum and Clonostachys rosea in real-time. Commun. Biol. 4, 262. ( 10.1038/s42003-021-01767-1) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 74.Kuhn T, Mamin M, Bindschedler S, Bshary R, Estoppey A, Gonzalez D, Palmieri F, Junier P, Richter XYL. 2022. Spatial scales of competition and a growth–motility trade-off interact to determine bacterial coexistence. Figshare. ( 10.6084/m9.figshare.c.6316842) [DOI] [PMC free article] [PubMed]

Associated Data

This section collects any data citations, data availability statements, or supplementary materials included in this article.

Data Citations

  1. Kuhn T, Mamin M, Bindschedler S, Bshary R, Estoppey A, Gonzalez D, Palmieri F, Junier P, Richter XYL. 2022. Spatial scales of competition and a growth–motility trade-off interact to determine bacterial coexistence. Figshare. ( 10.6084/m9.figshare.c.6316842) [DOI] [PMC free article] [PubMed]

Data Availability Statement

All data supporting the reported results can be found in the data tables in the manuscript and the electronic supplementary materials [74].


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