Universal entrainment mechanism governs contact times with motile cells
Arnold Mathijssen, Rapha\"el Jeanneret, Marco Polin

TL;DR
This study uncovers a universal physical mechanism, based on Taylor dispersion, that governs contact times between motile cells and particles, influencing biological interactions like predation and infection.
Contribution
The paper demonstrates that particle entrainment by motile cells is a universal phenomenon explained by a physical model combining experiments, simulations, and analytical theory.
Findings
Entrainment length depends on a balance of advection and diffusion.
Optimal particle size for entrainment is predicted and experimentally confirmed.
Flagella organization and swimming speed affect contact times.
Abstract
Contact between particles and motile cells underpins a wide variety of biological processes, from nutrient capture and ligand binding, to grazing, viral infection and cell-cell communication. The window of opportunity for these interactions is ultimately determined by the physical mechanism that enables proximity and governs the contact time. Jeanneret et al. (Nat. Comm. 7: 12518, 2016) reported recently that for the biflagellate microalga Chlamydomonas reinhardtii contact with microparticles is controlled by events in which the object is entrained by the swimmer over large distances. However, neither the universality of this interaction mechanism nor its physical origins are currently understood. Here we show that particle entrainment is indeed a generic feature for microorganisms either pushed or pulled by flagella. By combining experiments, simulations and analytical modelling we…
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††thanks: A.M. and R.J. contributed equally to this work and are joint lead authors. \arA.M., R.J. and M.P. designed the study, analysed results, developed the theory, wrote the manuscript; R.J. performed the experiments; A.M. developed the model, performed simulations.††thanks: \ar R.J. Current Address: IMEDEA, University of the Balearic Islands, Carrer de Miquel Marquès, 21 07190 Esporles, Illes Balears
Universal entrainment mechanism controls contact times with motile cells
Arnold J. T. M. Mathijssen
Department of Bioengineering, Stanford University, 443 Via Ortega, Stanford, CA 94305, United States
Raphaël Jeanneret
Physics Department, University of Warwick, Gibbet Hill Road, Coventry CV4 7AL, United Kingdom
Marco Polin
Physics Department, University of Warwick, Gibbet Hill Road, Coventry CV4 7AL, United Kingdom
Abstract
Contact between particles and motile cells underpins a wide variety of biological processes, from nutrient capture and ligand binding, to grazing, viral infection and cell-cell communication. The window of opportunity for these interactions depends on the basic mechanism determining contact time, which is currently unknown. By combining experiments on three different species -Chlamydomonas reinhardtii, Tetraselmis subcordiforms, and Oxyrrhis marina- simulations and analytical modelling, we show that the fundamental physical process regulating proximity to a swimming microorganism is hydrodynamic particle entrainment. The resulting \ardistribution of contact times \aris derived within the framework of Taylor dispersion as a competition between advection by the cell surface and microparticle diffusion, and predict\ars the existence of an optimal tracer size \arthat is also observed experimentally. Spatial organisation of flagella, swimming speed, swimmer and tracer size influence entrainment features and provide trade-offs that may be tuned to optimise \arthe estimated probabilities for microbial interactions like predation and infection.
I Introduction
The wide variety of microbial interactions is often deeply influenced by physics. Within biofilms, electric currents can coordinate cellular metabolic rates Prindle et al. (2015), while wrinkles draw nutrients by capillarity Wilking et al. (2013). Microscopic flow fields Drescher et al. (2010); Guasto et al. (2010); Drescher et al. (2011) can lead to large-scale collective motion Zhang et al. (2010); Cisneros et al. (2010); Sokolov and Aranson (2012) with enhanced drug resistance Lai et al. (2009); Butler et al. (2010), surprising rheological properties Sokolov and Aranson (2009); Rafaï et al. (2010); López et al. (2015), and global features controllable by structured confinement Wioland et al. (2013); Mathijssen et al. (2016); Ravnik and Yeomans (2013); Lushi et al. (2014); Mathijssen et al. (2015a). When coupled with population-wide taxis, these flows result in macroscopic instabilities Platt (1961); Plesset and Winet (1974); Pedley et al. (1988) which increase nutrient fluxes Tuval et al. (2005) and can \arprovide unexpected new avenues for capture and manipulation of small objects Dervaux et al. (2016).
For swimming microorganisms, many interactions hinge on close contact. \arThese include fundamental processes like nutrient uptake Magar et al. (2003); Michelin and Lauga (2011); Tam and Hosoi (2011); Doostmohammadi et al. (2012); Lambert et al. (2013); Ishikawa et al. (2016); Dölger et al. (2017); Short et al. (2006); viral and fungal infection of microorganisms of ecological and commercial importance Seisenberger et al. (2001); Taylor and Buckling (2013); Carney and Lane (2014), eukaryotic fertilisation Riffell and Zimmer (2007); and grazing, which happens on natural preys Roberts et al. (2010); Davidson et al. (2011); Gilpin et al. (2017); Dölger et al. (2017) as well as marine microplastics Cole et al. (2013); Wright et al. (2013), and is recently being discovered as a fundamental behaviour in many strains of motile green algae until recently regarded as exclusive phototrophs Maruyama and Kim (2013); Carney and Lane (2014); Selosse et al. (2017). With the exception of complex feeding currents in ciliates like Vorticella Pepper et al. (2010, 2013) or Paramecium Jung et al. (2014); Zhang et al. (2015), the window of opportunity for these microbial interactions to take place will depend on a finite contact time . For a constant success rate per unit time , the probability that the interaction is successful is given by Gilpin et al. (2017). Large values of will be favoured by long contact times, and will therefore depend on the physics that regulates proximity. Although the theoretical basis of contact times is still developing Bally et al. (2011); Banerjee et al. (2016); Xu and Shaw (2016), it is reasonable to expect that a key role will be played by the properties of the near field, the region close to the cell body Dölger et al. (2017). As already noted in this context by Purcell Purcell (1977), the fluid layer close to a swimming microorganism is expected to be carried along by it. Small objects sufficiently close to a microswimmer are therefore entrained Darwin (1953) and stay in close contact with it for the time required to escape the near-field region. Entrainment converts a temporal quantity, the contact time , into a readily measurable spatial quantity, the entrainment length . While recent studies have provided numerical support for particle entrainment by microorganisms Pushkin et al. (2013); Mueller and Thiffeault (2017); Shum and Yeomans (2017), experimental evidence is limited to the microalga Chlamydomonas reinhardtii Jeanneret et al. (2016), and it is not clear whether or not this phenomenon is a general feature of microbial motility. At the same time, there are currently no theoretical predictions for the duration of these contact events, as a clear picture of the physics underlying entrainment is lacking Lin et al. (2011); Pushkin et al. (2013); Jeanneret et al. (2016); Thiffeault (2015); Mueller and Thiffeault (2017); Shum and Yeomans (2017).
Here we combine experimental, numerical and theoretical approaches to investigate particle entrainment by microorganisms. \arExperiments with the green microalgae Chlamydomonas reinhardtii (CR) and Tetraselmis subcordiforms (TS) -pulled by different numbers of anterior flagella- and the dinoflagellate Oxyrrhis marina (OM) -pushed by a posterior flagellum- demonstrate that entrainment is indeed a robust generic feature amongst swimming cells, whose existence is independent of the propulsion strategy. Entrainment is shown to be a direct consequence of two universal traits: advection by a no-slip cell surface, as recently suggested in Mueller and Thiffeault (2017), and particle diffusion. A first-passage Taylor-dispersion argument combines these fundamental physical ingredients, allowing for analytical estimates of the mean contact time and the full entrainment distribution, while offering an intuitive understanding of the observed existence of an optimal particle size for entrainment. We conclude by discussing potential consequences on the probability of successful interactions.
II Nearby object-microswimmer interactions are governed by a universal entrainment mechanism
When inspecting tracer dynamics at large magnification () and high framerate ( fps), very similar entrainment events are observed for all our organisms, regardless of their propulsion mechanism or generated flow. Examples of typical trajectories with particle radius r_{\textmd{\tiny{P}}}=0.5\nobreak\mbox{~{}\mum} are shown in Movies S1-3, for CR, TS and OM respectively at [url to be inserted] . This mechanism is best understood from the viewpoint co-moving with the swimmer. After an almost head-on collision, a bead reaches a region near the cell surface, Fig. 1a). It travels slowly around the body approximately following streamlines from front to back, and eventually leaves behind the organism, Fig. 1b,c). Since the only common physical feature of these organisms is the presence of the cell body surface, we propose that entrainment is only the consequence of the no-slip layer that this boundary induces. Therefore, the particle is hydrodynamically coupled to the swimmer in this layer and resides in its vicinity for an extended duration, the contact time . In the laboratory frame, the particle is then displaced a distance in the direction of motion. Hence, the average contact time and entrainment length are directly related via
[TABLE]
To quantify our observations, we measure the distribution of for different swimmers, Fig. 1e) \ar and 1e)-Inset. These \ar have all a similar shape, indicating a common underlying mechanism, with \aran exponential-like decay of length scale above the length at the peak of the distribution. Exponential fits to these curves give L_{\rm J}^{\rm(CR)}=9.2\pm 0.6\nobreak\mbox{~{}\mum} for CR, L_{\rm J}^{\rm(TS)}=7.4\pm 1.2\nobreak\mbox{~{}\mum} for TS and L_{\rm J}^{\rm(OM)}=11.7\pm 1.4\nobreak\mbox{~{}\mum} for OM, while we find L_{\rm M}^{\rm(CR)}\approx 6.7\nobreak\mbox{~{}\mum}, L_{\rm M}^{\rm(TS)}\approx 8.6\nobreak\mbox{~{}\mum} and L_{\rm M}^{\rm(OM)}\approx 7.5\nobreak\mbox{~{}\mum}.
\ar
Unexpectedly, the characteristic entrainment length is significantly smaller for TS than CR despite a slightly larger body size. As described also in Appendix B, this effect is mainly attributed to the larger number of flagella in TS, which limit the average contact time by either rapidly pushing the beads backwards during the power stroke (Movie S2) or by ejecting them out of the no-slip layer during the recovery stroke. However, at the same time, front-mounted flagella can reach out and pull beads towards the body, widening the effective cross-section for entrainment around the swimming path. This is reflected in , the distribution of rescaled impact parameters, , before entrainment. For both TS and OM, can be described accurately by a single exponential decay with characteristic lengths and (Fig. 1g,h)). However, with CR, structurally very similar to TS but with a single pair of flagella, the distribution shows two markedly distinct behaviours for impact parameters above and below the cell body radius. For , follows the curve characteristic of TS; below that threshold we observe instead an exponential decay with a significantly smaller characteristic length . This is a consequence of the fact that, in CR, entrainments below are \arby and large a consequence of “pure” collisions with the cell body, without appreciable influence from flagella. Flagella participate instead in entrainment events with relatively large impact parameters, by increasing significantly their abundance over what would otherwise be expected. In order to study the main entrainment mechanism for CR, in the following we will focus on jump events with when comparing with numerical data. These include of all the entrainments observed.
The outboard swimmer model captures the entrainment mechanism faithfully. Figures 1c,d) show that simulated tracer trajectories reproduce well the experimental ones. In particular, we see that in both cases the particles tend to detach close to the swimming axis despite the variation in initial impact parameter, here randomly chosen in (see also Movies S4,5 for CR and OM resp. and Movie S6 for a comparison \arwith a model Escherichia coli (EC)). More quantitatively, the PDF of entrainment lengths from simulations agrees very well with the experimental one in Fig. 1f), \arwhen equivalent quantities are compared (i.e. the projection of the three-dimensional jump onto the focal plane). Note that the entrainment length is globally overestimated (L_{\rm M}^{\rm(sim)}\approx 14.5\nobreak\mbox{~{}\mum} and L_{\rm M}^{\rm(exp)}\approx 9.4\nobreak\mbox{~{}\mum}), \arwhich we attribute to the approximations of this minimal model and the effect of flagella as discussed above.
III Steric interactions reduce the contact time of large particles
In light of these findings about the entrainment mechanism, we will now develop a simple theory to predict contact times. A detailed derivation is given in Appendix D. We consider small particles that do not disturb the swimming direction significantly, which is a reasonable assumption if Shum and Yeomans (2017) as supported also by our experiments. A streamline along the swimmer body can be approximated as
[TABLE]
written in spherical coordinates of the reference frame co-moving with the swimmer, Fig. 1b). Close to the cell body the advection of tracers is then governed by the tangential flow, . Evaluating along a streamline with impact parameter gives the velocity of a particle,
[TABLE]
where is the closest distance of approach, Fig. 1b), and characterises the flagellar distance from the body ( for OM, CR and EC respectively, see Appendix C). Then, in the deterministic limit, the contact time is found by integrating the inverse velocity along the particle trajectory, , where is the arclength differential. Since the velocity satisfies the no-slip condition at the cell surface, tracers with a small distance of approach move around the body slowly (Eq. 3) which increases the contact time. As the minimum distance is dictated by the finite size of the particle, larger tracers are expected to experience stronger tangential flows and therefore smaller contact times.
IV Brownian noise limits entrainment of small particles
Together with particle advection, it is important to consider the presence of thermal noise. We first explore its effect by simulating outboard swimmers with tracers subjected to Brownian motion (Movies S4-6 at [url to be inserted] ). Figure 2 shows how the spatial PDF of an ensemble of tracers initially in front of the microorganism depends on tracer size. Small tracers spread far from the swimmer and do not efficiently access the no-slip layer (Fig. 2a)). Consequently, they are exposed to stronger tangential flows, limiting the contact time. Large tracers do not diffuse away but cannot approach the no-slip surface closely, as described previously and illustrated by the inaccessible region around the cell body (Fig. 2d)). Instead, we see a maximum in the contact time for beads of intermediate size, which concentrate most tightly around the moving cell (Fig. 2b,c)). Optimal entrainment is systematically observed in simulations of both OM and CR, with optimal tracer radii r_{\rm P}^{*}\sim 0.4,0.3\nobreak\mbox{~{}\mum} respectively (Fig. 3a)). Moreover, whereas these organisms can move particles along for body lengths, entrainments by the EC model do not exceed \sim 1.2\nobreak\mbox{~{}\mum} for any tracer size. The super-linear growth of the average jump length on cell size (Fig. 13c in Appendix D; see also Mueller and Thiffeault (2017)) strongly restricts particle transport for micron-size organisms, and is consistent with the lack of previous reports of strong entrainment by bacteria Wu and Libchaber (2000); Ishikawa et al. (2010); Kasyap et al. (2014); Jepson et al. (2013).
Experiments with CR for a range of different tracer sizes confirm the existence of a maximum in entrainment length (Fig. 3b)), with diffusion-dominated tracer trajectories below, and steric-interaction-limited paths above, the optimal size r_{\rm P}^{*}\sim 0.7\nobreak\mbox{~{}\mum}. These features are observed in simulations also when considering tracers that are initially located at random impact parameters within , rather than directly in front of the cell (Fig. 3b) inset). Altogether, the semi-quantitative agreement on both the location of the maximum and the values of jump lengths suggests that our outboard model captures the essential physics behind the entrainment mechanism.
V Optimal size for contact time
Results from experiments and simulations can be rationalised with an approach akin to Taylor’s dispersion Taylor (1953); S. et al. (2004). Consider a Brownian particle advected in a linear shear flow over a straight solid surface that mimics the swimmer’s cell wall, Fig. 4a). The flow velocity is , where the strain rate, , derives from the velocity along a streamline given by Eq. 3. A particle of radius is initially positioned at , disperses with \ar thermal diffusivity and is advected by the flow , but cannot cross the line . Without loss of generality, this is mapped to an unbounded “image” system Van Kampen (1983) where the particle is initially located at , the modified flow is , and the tracer can diffuse everywhere (Fig. 4b)). \arOur first aim is to estimate the average time needed for the colloid to travel a distance along the positive -direction, imitating a journey around the swimmer’s body. The \ar motion of the colloid is described by
[TABLE]
where \ar is a Gaussian white noise satisfying and . Integrating and ensemble averaging Eq. 5 (\arsee Appendix D), leads to
[TABLE]
\ar
and requiring that , the mean contact time becomes the solution of the cubic equation
[TABLE]
\ar
This can be solved analytically using Cardano’s formula (Eq. 50 Appendix D) and then converted into the average entrainment length with Eq. 1. Figure 3a) compares the results for CR, OM and EC (solid lines) when employing the same parameters used in the simulations, and shows that this simple approach recovers the correct qualitative non-monotonic behaviour of the average entrainment length, as well as the position of the entrainment maxima. The predicted magnitude of the entrainment length deviates by a factor of near the maxima, due mostly to an overestimate of the average tangential speed experienced by the tracer (see Fig. 13a and Appendix D4). \arFor either decreasing or increasing , this simple estimate recovers the correct deterministic limit, in which becomes independent of (\arFig. 3c) dashed lines; see Appendix D2 and Mueller and Thiffeault (2017)). However, as thermal noise becomes important, and (Fig. 3c) solid line): slower organisms should display shorter entrainment lengths because particles diffuse away before being displaced substantially. Altogether, these results suggest already that Brownian motion can have \ar significant effects on the entrainment efficiency.
\ar
A simple argument can also recover the optimal tracer size and its dependence on the swimmer’s size and speed. Fig. 3d) presents a map of , obtained by optimising the contact time (Eq. 7) with varying and but fixed . On one hand, increasing swimmer speed shifts to lower values, because faster advection limits the importance of Brownian motion. On the other hand, increasing swimmer size increases , because the larger distance to travel around the cell enhances the relative effect of diffusion. A simple estimate for the optimal particle size is found by comparing a characteristic diffusion time \ar and a characteristic advection time from Eq. 3. Defining the entrainment Péclet number as \ar, where , the optimal tracer size corresponds to , which yields
[TABLE]
\ar
Using experimental parameter values, this expression predicts r_{\rm P}^{*}\sim 0.8\nobreak\mbox{~{}\mum} for CR, which compares well with the value \sim 0.7\nobreak\mbox{~{}\mum} found experimentally; and recovers the power laws describing the dependence of on and observed in numerical solutions of Eq. 7 (Fig. 14 in Appendix D).
\ar
Notice that in many natural situations both parties can be active, and active motion of the small species could affect the duration and optimality of the contact process substantially. Considering as an example a system with a large predator and a small motile prey, the velocity and reorientation timescale of the latter lead to an effective diffusion coefficients , which can easily be times larger than for typical bacteria Berg (1993); Saragosti et al. (2012). The modified entrainment Péclet number can be significantly smaller than the previous one, indicating a possibly substantial decrease in contact time. Therefore, even though prey motility increases encounter rates with predators Almeda et al. (2016), it could nonetheless reduce the overall probability of being captured.
VI The contact time distribution
\ar
The previous section provides a simple description of the average motion of a colloidal particle, based on its advection along the swimmer’s body at an effective speed that depends on the particle’s average distance from the swimmer Eq. 5. This 1D parallel can in fact be pushed further to describe the whole distribution of entrainment lengths in Fig. 1e,f). In the spirit of G. I. Taylor’s work on diffusion within a pipe Taylor (1953), the 2D motion of the entrained colloids in Fig. 4a,b) (described by Eq. 5) can be reduced to a 1D advection-diffusion process with an effective velocity and diffusivity (see Appendix E). For this system, the distribution of first arrival times to a downstream boundary at a distance is well known, and can then be translated with Eq. 1 into the entrainment length distribution:
[TABLE]
This functional form provides an excellent fit to all the experimental distributions recorded (see Fig. 1f) and Fig. 15a,b) in Appendix E), confirming that the main entrainment behaviour can indeed be studied within this simplified framework. Simple analytical estimates for and can then be found by approximating the 2D advection-diffusion process as being confined within a uniformly sheared region of appropriate thickness (Appendix E):
[TABLE]
where and w=(\langle\epsilon\rangle-r_{\textmd{\tiny{P}}})(1{\color[rgb]{0,0,1}+}\sqrt{\pi/2-1}) are the average position and estimated spread of the particle distribution above the swimmer’s surface at time . The comparison between the fitted and calculated values of and for the different tracer sizes probed with CR in Fig. 4c) shows that this simple description captures well the qualitative dependence of the experimental entrainment length distributions on tracer size; and provides an accurate prediction for , which corresponds to the minimum of . At the same time, Fig. 4c) shows that the parameter appears to be globally underestimated by m. This is likely the result of the approximations involved in the derivation of Eq. 11 rather than a consequence of factors like electrostatic interactions (the Debye screening length in the algal media is easily estimated to be always nm).
\ar
An experimentally validated model of the entrainment process allows us to rationalise experimental features of the measured distributions, and explore qualitatively their dependence on system parameters in lieu of labour-intensive experiments. On one hand, it is easy to see that the part of the distribution in Eq. 10 past the maximum can indeed be described well by a single exponential decay if the parameters provide a sufficiently large value of the effective Péclet number . This is what we observe in Fig. 1e,f).
\ar
The same quantity also controls the effect of fluctuations, represented by the relative spread of the distribution of entrainment lengths, . This implies that slower cells will feature a wider distribution of entrainment lengths, and therefore contact time, as the effective diffusion plays a relatively larger role than in fast-moving cells (see Fig. 5a)). Similarly, small tracers feature larger deviation relative to their average contact time due to the dominant effect of the effective diffusion.
\ar
In turn, these fluctuations can have some effect on the likelihood of interactions that take place during entrainment. From the contact time distribution we can analytically extract the probability of success for a given cell-object interaction in two simple illustrating examples: i) the case where the interaction requires a minimum time of contact and ii) the case of a constant success rate per unit time. In the first case, the success probability (SP) is given by
[TABLE]
which is shown Fig. 5b) for three different tracer sizes using the experimental CR parameters. For large particles the contact time does not deviate much from its average value (), and the SP follows a switch-like dependence on the interaction time (green curve), where the switching time is the average contact time (dashed lines). However, as the particle size decreases below the optimal size (i.e. ), the fluctuations enhance the chance of success for slow interactions (i.e. ), and small particles (red curve) can be more successful than those with the largest average contact time (blue curve) at slow interactions, but at the cost of reduced success for faster interactions. In the second case, the success probability is
[TABLE]
shown in Fig. 5c) for the same tracer sizes. Here we observe that fluctuations do not play a significant role. Regardless of the rate of success , the chance of success will always be optimal for the tracer with the largest average contact time (Eq. 7). Despite their simplicity, these examples already portray the interesting role that the noisy entrainment process can play in different types of natural interactions.
VII Conclusion
Swimming microorganisms vary greatly both in body size and in the details of their propulsion, from the number and arrangement of flagella to their gaits. Yet, despite this variability, our results show that particle entrainment is a remarkably universal mechanism. Combining experiments with numerical simulations, we see that pullers and pushers entrain particles with similar efficiency. We see no evidence for either “wake bubble” effects Lin et al. (2011), or entrainment due to a stagnation point in front of the cell Jeanneret et al. (2016); Thiffeault (2015). Instead, our results suggest that entrainment is a consequence of an organism’s no-slip surface, a characteristic shared by the three species we study here. This feature, recently suggested also in Mueller and Thiffeault (2017), is consistent with the lack of entrainment in numerical studies involving squirmers, which instead propel with a surface slip velocity Lin et al. (2011); Thiffeault (2015). Accordingly, we predict that ciliates like Paramecium and multicellular algae like Volvox will not substantially entrain micron-sized objects, since they swim by an effective surface slip generated by thousands of cilia and flagella. Studies of V. carteri swimming through a colloidal suspension support this hypothesis (see supplementary movie from Drescher et al. (2010)). Comparing different species, we also see that the flagellar arrangement has a quantitative effect on particle entrainment. Front-mounted flagella decrease the average contact time but increase the interaction range, and are therefore likely to increase the frequency of entrainments.
The outboard model proves to be in fair qualitative and quantitative agreement with our experimental results. It provides directly comparable tracer dynamics and, crucially, \arit reproduces successfully the shape of the entrainment length distribution. This strongly suggests that the model \ar captures correctly the essential physics, with further support provided by the maximum in the entrainment length over particle size observed in both experiments and simulations. \ar These results can in fact be accurately described by a simple Taylor-dispersion theory, which provides the correct functional form for the entrainment distribution with parameters that can be estimated semi-quantitatively through simple approximations. The theory, which is based exclusively on Brownian diffusion within the high-shear layer close to the swimmer’s surface, provides an intuitive justification for the existence of an optimal particle size for entrainment, , set by the balance between diffusive and advective timescales.
Size-dependent contact times might affect predation by microorganisms. Experimental studies of microbial grazing indicate that this is indeed a selective process Montagnes et al. (2008). For example, Oxyrrhis marina feeds on prey ranging from bacteria to cells as large as itself Flynn et al. (1996); Roberts et al. (2010), but seems to have an optimal prey size Hansen (1992); Hansen et al. (1996); Roberts et al. (2010); Davidson et al. (2011), in agreement with our hydrodynamic arguments. Phagotrophic selectivity is complex, \arand surprisingly common even amongst microbial species historically considered exclusive autotrophs (e.g. some green microalgae Selosse et al. (2017)). It certainly depends on many factors including chemical cues and cell surface properties. However, the physics leading to the non-monotonic size-dependence of contact time is inescapable, and therefore needs to be taken into account. A non-monotonic dependence on tracer size has also been reported for the effective diffusion of colloidal particles suspended within an E. coli culture Patteson et al. (2016). These experiments, which focus on particles larger than the microorganisms, show that potentially new mechanisms could be at play in that size range.
To conclude, we have seen that particle entrainment is a generic feature of the interaction between microorganisms and small particles, and have characterised the physics behind it. A complete picture of these interactions, however, will require to integrate our results not only with those from intermediate and far-field studies Pushkin et al. (2013); Mathijssen et al. (2015b), but also with a thorough characterisation of the navigational strategy of the microorganism Méndez et al. (2013). This will enable more accurate bottom-up models of microbial grazing, which can be used to predict feeding or clearance rates by phagotrophs Dölger et al. (2017), and potential trade-offs between feeding and swimming Strathmann and Grünbaum (2006); Michelin and Lauga (2011); Gilpin et al. (2017). At the same time, prolonged contact also underpins the successful binding of viruses and other parasites to cells Seisenberger et al. (2001). By showing that the contact time with motile microorganisms is limited, s for reasonable swimmer sizes and speeds, we suggest that motility can potentially affect infection rates Taylor and Buckling (2013) and thus provide a fitness advantage. This should be true in particular for ciliates, which display an effective surface slip and therefore a faster clearance of particles. Targeted experiments and modelling efforts in this area will improve our mechanistic understanding of early infection events in microorganisms.
From a micro-engineering perspective, our model shows that entrainment lengths become millimetric or even larger for micrometric tracers when considering swimmers or active particles with radius r_{\textmd{\tiny{S}}}\gtrsim 50\nobreak\mbox{~{}\mum}. When combined with externally triggered reorientation events, this purely hydrodynamic phenomenon could enable cargo transport by self-propelled colloids without requiring any surface functionalisation.
Acknowledgements.
We are grateful to Kirsty Wan and Raymond Goldstein for sharing the initial culture of TS, \arand to an anonymous Referee for encouraging us to search for an analytic expression of the distribution of entrainment lengths. This work was supported in part by and ERC Advanced Grant (291234 MiCE) \arand the Human Frontier Science Program (Fellowship LT001670/2017) (A.M.); and a Royal Society Research Grant (RG150421) (M.P.).
Appendix A Experimental methods
A.1 Introduction to the microorganisms
We have considered 3 different species of flagellated eukaryotic unicellular microorganisms presenting different features of swimming but having roughly the same body-size: Chlamydomonas reinhardtii (CR), Tetraselmis subcordiforms (TS) and Oxyrrhis marina (OM). CR and TS are both green algae with a very similar prolate body shape but differing in the number of flagella in front of their body: 2 for CR and 4 for TS. CR uses most of the time a breaststroke way of swimming Polin et al. (2009), while TS flagella beat successively in a transverse gallop fashion Wan and Goldstein (2016). They are puller-like microorganisms Lauga and Powers (2009); Guasto et al. (2010); Klindt and Friedrich (2015). The length and width of their body are respectively m and m for CR, m and m for TS. In the (confined) microfluidic channels (thickness m) used for the experiments, the average speed of these microorganisms were: m.s*-1* and m.s*-1*. OM is a dinoflagellate widely distributed across the seas (except the polar areas). During the past twenty years it has become a model organism for studying predator-prey interactions at the micro-scale. It also has a prolate shape but is bigger and more asymmetric than CR and TS. We measured an average length m, an average width m and an average speed (in a m-thick channel) m.s*-1*. This microorganism has 2 flagella at the back of its body a long and a short one. The long one is used to propel while the short transverse one is used to turn and appears to be a tool to catch and recognize preys. We chose this microorganism as a representative of eukaryotic pusher-type swimmers Kiørboe et al. (2014).
A.2 Cultures of the microrganisms
Cultures of CR strain CC125 were grown axenically in a Tris-Acetate-Phosphate medium at C under periodic fluorescent illumination (, OSRAM Fluora) with a dark/light cycle of 12h/12h. This is done to synchronize the cell cycles among the population. Cultures were kept in the exponential phase (concentration of cells/ml) by transferring daily the algae into a new flask of fresh-medium.
Cultures of TS strain CCAP 161/1A were grown axenically in a Seawater Nutrient Broth medium at C under fluorescent illumination (, OSRAM Fluora). Cultures were kept at a concentration of cells/ml by transferring biweekly the algae into a new flask of fresh-medium (growth rate cells/day).
Cultures of OM strain CCAP 1133/5 were grown monoxenically in a f/2 medium at C together with the small alga Nannochloropsis oculata (CCAP 849/1) serving as food. Fresh medium and algae were supplied to the culture every months.
When performing the experiments, cultures were harvested in the exponential phase ( cells/ml for CR and TS, cells/ml for OM).
A.3 Experimental setup
After gently centrifuging the suspension of a given organism, the supernatant was replaced by the appropriate fresh medium also containing a small fraction of colloids (Polysciences, catalog no. 19819-1) of the required radius (m for TS and OM, m for CR) at a concentration solids. These polystyrene particles present carboxyl groups on their surface which contribute to prevent adhesion to the microorganisms. The suspension was then loaded into a PDMS based microfluidic chip having a visualisation chamber mm wide and m (for CR and TS) or m thick (for OM). Given the size of the organisms and the thickness of the chambers, there was enough room for the particles to travel over or beneath the swimmers around their bodies, making the entrainment mechanism fully 3D. This justifies the 3D numerical approach as the near-field flows are not expected to be influenced by the presence of confining walls. Because the colloidal suspension was very diluted and the depth of focus thick enough, we were still able to track the colloids before and after entrainment and extract accurately the entrainment lengths. The channels were previously passivated with w/w BSA solution in water. The inlets of the chips were sealed with Vaseline to prevent evaporation.
The systems were recorded at fps using a Pike camera (F-100B, AVT) under phase contrast illumination on a Nikon TE2000-U inverted microscope. A long-pass filter (cutoff wavelength 765 nm) was added to the optical path to prevent phototactic response of CR and TS. \arThe magnification was set according to the size of colloids: for tracer radii of and m, for m tracers and for m tracers. We limited the experimental investigation of the influence of tracer sizes on the entrainment to this size range because: i) visualisation of tracers smaller than requires fluorescence, which influences the behaviour of the algae; ii) tracers larger than influence the motion of the microorganisms, probably due to mechanosensation. This is an interesting range to explore but outside the scope of the present study. Despite these constraints, the data in both Fig. 3b and 4c display clearly the non-monotonic dependence of entrainment on particle size, with an optimum at a radius comparable to the predictions of both outboard model and the theoretical model.
Organisms and colloids trajectories were then digitised using a standard Matlab particle tracking algorithm (The code can be downloaded at http://people.umass.edu/kilfoil/downloads.html). Individual jumps were extracted from the trajectories with the same procedure as our previous work Jeanneret et al. (2016), \ar which was complemented by a visual inspection of every single events in order to filter out non-entrainment perturbations. This extra step was not present in Jeanneret et al. (2016). For the experiments with CR, we have extracted the following number of jump events for each particle size: 388 for , 303 for , 311 for and 135 for .
Appendix B On the effect of flagella
To quantify the role of the flagella on the entrainment process, we first consider the impact parameter \arpreceding the entrainment. It has to be noted here that in the experiments we can only measure the projected impact parameter on the focal plane due to the lack of vertical resolution for both the swimmers and the colloids. However, as will be clear in what follows, this measurement allows to extract insightful information. The PDF of impact parameters of organism-tracer encounters conditioned to the fact that the beads will be entrained is shown Fig. 1g-main text for the three organisms after rescaling by the half-width of the organisms (see Fig. 1h-main text for a semi-log plot). These PDFs are \arsimilar for the three swimmers and can be well fitted by exponential distributions. However, the characteristic decay obtained for TS is larger than that of CR and OM: while and , showing that TS can entrain particles even when those are relatively far away from the swimming path. We interpret this results as a consequence of the transverse gallop beating pattern of the four flagella of TS, \arincreasing the probability of the beads being brought by these appendages towards the body, whatever the impact parameter, small or large. This is not true for OM and CR for which we observe more peaked distributions around , showing that particles \arare much more likely to be entrained if close to the swimming path. However, the distribution for CR presents a clearly visible bump above , also observed with other tracer sizes, Fig. 6a. This increase in the probability of entrainment at larger is also explained by the presence of flagella that bring the beads towards the no-slip layer of the cell. \arThis effect is much less important for CR because it only has two flagella.
Finally, we expect the entrainment length to decrease with impact parameter, because the larger the impact parameter the larger the parameter (Fig. 1b-main text) and consequently the further from the no-slip surface the bead will travel. To probe for this effect, \arwe plot in Fig. 6b the entrainment length : the average displacement for impact parameters vs. . This reduces considerably the noise compared to simply looking at the average length at any given impact parameter. This quantity depends very weakly on for the quadriflagellate TS, showing that the entrainment length is a weak function of impact parameters. Again this is due to the flagella bringing the beads towards the no-slip surface but in an unpredictable manner: the beads reach the no-slip surface at random polar angles (Fig. 1b-main text) whatever the impact parameter . For the biflagellate CR, we observe an interesting behavior where this quantity first decreases substantially up to a\sim 3-4~{}\nobreak\mbox{~{}\mum}\sim w^{(CR)}/2 while above the curve flattens. At small impact parameters the flagella do not play a role and the beads arrive at the surface of the cell in a more predictable way following relatively well defined pathlines. However at larger impact parameters, the flagella have an effect akin to TS and \arrender the entrainment length more uniform. For the pusher OM we seem to observe a decreasing curve with a constant slope, consistent with our interpretation of the role of the flagella with CR and TS. However the more unfrequent entrainment events for this organism limit substantially the statistics.
Appendix C \arOutboard model for entrainment
Here we present the ‘outboard propulsion’ model to evaluate the flow fields generated by a micro-swimmer, which we use later to perform simulations with tracer particles. This name implies that all propulsion forces are transmitted to the liquid from outside the cell body, as opposed to be generated at the swimmer surface. For example, the helical flagellum of a bacterium bears resemblance to an outboard motor, while CR takes after a rowing boat. To capture the near-field flows of an organism, we use a finite-sized spherical body (radius ) with a no-slip boundary condition at its surface. Propulsion is achieved by a set of regularised Stokeslets outside the body, whose flow satisfies the no-slip condition on the cell body. The number, arrangement and motion of the driving forces is species specific. Instantaneous swimming speed and rotation derive from the requirement of zero net force and torque. This model will be used to simulate an actively beating CR, a steady OM, and a steady E. coli (EC) bacterium for comparison.
\ar
Our approach is inspired by previous work Bennett and Golestanian (2013); Friedrich and Jülicher (2012); Brumley et al. (2014); Dölger et al. (2017), and is similar to the one developed at the same time by Mueller and Thiffeault Mueller and Thiffeault (2017), who implemented a two time-dependent point-force model with a finite-sized no-slip body to simulate Chlamydomonas cells.
C.1 Model for Chlamydomonas
We first consider \arCR with a body that satisfies the no-slip boundary condition at its surface, and two beating flagella (see Fig. 7). The cell body is modelled as a solid sphere of radius that is located at position at time and oriented in the direction, in Cartesian coordinates. The flagella are represented by two point forces (Stokeslets) that move along the trajectories and in the plane, where both flagella exert an equal force . Here, and the swimming stroke is parametrised by the beat cycle angle with a stroke frequency of . We assume that CR that does not rotate about the axis, so that is purely along the direction. This assumption can be relaxed straightforwardly.
The swimmer moves with a velocity along the axis, where the velocity is taken from the measurements in Ref. (Guasto et al., 2010, Fig. 4b), but reduced by a factor of 0.7 to account for the confinement in our experiments. Note that the swimmer velocity oscillates throughout the stroke period, where the speed averaged over a swimming stroke is \langle v_{\textmd{\tiny{S}}}\rangle\approx 84\nobreak\mbox{~{}\mu{}^{-1}}. The distance progressed per stroke is d_{\textmd{\tiny{S}}}\approx 2.25\nobreak\mbox{~{}\mum} with a forward : backward motion ratio .
The flow field of the simulated microswimmer is the superposition of the flow from the spherical cell body, , and that from the two flagella, . The former is obtained from the well known solution to a no-slip sphere dragged at speed through a viscous fluid, which in the co-moving frame is:
[TABLE]
where and . Unless otherwise mentioned, we will use r_{\textmd{\tiny{S}}}=3.5\nobreak\mbox{~{}\mum} for CR throughout this work.
The flagella are modelled as point forces, which in presence of the no-slip spherical body generate the flow . Here is the Green’s function for the no-slip sphere system (see Spagnolie et al. (2015)). The flagellar force is then related to the swimmer velocity through the requirement of zero net force on the system. This can be imposed by subtracting from the total flagellar force the net force exerted by it on the body
[TABLE]
where the integral runs over the surface of the microorganism, and is the stress tensor of the flagellar flow field. As a result, the net force exerted by the flagellum on the fluid becomes , with
[TABLE]
depending on the relative position between the flagella and the body, , and the distance . Balancing the flagellar and body forces on the fluid one obtains the relation between the instantaneous swimming velocity and the instantaneous flagellar force:
[TABLE]
Note that during the simulations of tracer particles near the model swimmer, the singularities of the external Stokeslets are regularised by capping the tracer’s advection speed to the organism’s speed. We have tested simulations with different cut-off values and cut-off descriptions, but we observe these lead to very similar results, because the amount of time a tracer spends close to the Stokeslets is short. We do not intend to capture flagellar interactions with great accuracy in these simulations, but we aim to have a good description of the no-slip layer flows close to the body, ensuring the overall flow is force-free. The swimmer-generated flow field, , is obtained by combining Eqs. C.1–20 for a prescribed flagellar trajectory . For CR we use a loop-like trajectory next to and mostly in front of the cell (Fig. 7), which is far from the body during the power stroke () and close to the body during the recovery stroke (). The resulting flow field is shown in Fig. 8 (time-resolved) and Fig. 9 (time-averaged); and in Supplementary Videos 7 and 8 in the lab frame and rest frame, respectively. These flows compare well with experimental measurements (see (Guasto et al., 2010, Fig. 3) and (Drescher et al., 2010, Fig. 3a)). They display a characteristic fluctuation, within a beat, between contractile (power stroke) and extensile (recovery stroke) behaviour, with a stagnation point at position which, in the limit , satisfies
[TABLE]
By solving this expression numerically, we superimpose the solution for as a red point in Fig. 8 and Video 1 throughout the beat cycle.
C.2 Model for E. coli
To model the time-averaged flow of the bacterium E. coli (EC), which is propelled by a rotating and left-handed helical flagellum of length \sim 6\nobreak\mbox{~{}\mum}, we consider a body radius r_{\textmd{\tiny{S}}}=0.5\nobreak\mbox{~{}\mum}, and represent the flagellum with steady Stokeslets located at , where , . The body moves with a constant swimming speed v_{\textmd{\tiny{S}}}=25\nobreak\mbox{~{}\mu{}^{-1}} along the axis. The body rotates with a constant angular velocity , balanced by the flagellar counter rotation represented here by four rotlets at the same positions . The Stokeslet and rotlet intensities, and are assumed to be the same across the point forces and torques, and are chosen to guarantee a system with zero net force and torque. The Stokeslet is selected following the reasoning of the previous section, leading to
[TABLE]
where
[TABLE]
To fix the rotlet , start from the rotational flow due to the body Kim and Karilla (1991):
[TABLE]
where . The full flagellar flow is given by
[TABLE]
The torque exerted by the -th rotlet on the fluid is , where
[TABLE]
Balancing the total torque on the fluid from the body and the rotlets, is found to be
[TABLE]
This fixes the representation Eq. 25 of the flow due to the -th component of the discrete flagellum. Together with the translation Eq. C.1 and rotation Eq. 24 of the body, this completes the model for EC. Fig. 10 shows the flow for the model of an E. coli bacterium, with flagellar Stokeslets and position \lambda=1.5\nobreak\mbox{~{}\mum}.
C.3 Model for Oxyrrhis marina
Lastly, we focus on the organism Oxyrrhis marina (OM), which is a dinoflagellate that propels by beating its posterior flagellum like a sperm cell. For simplicity, we use a time-averaged model with body radius r_{\textmd{\tiny{S}}}=9\nobreak\mbox{~{}\mum}, and the flagellum of length 48\nobreak\mbox{~{}\mum} is represented by four steady Stokeslets located at , where , \lambda=12\nobreak\mbox{~{}\mum}, and the body moves with constant swimming speed v_{\textmd{\tiny{S}}}=100\nobreak\mbox{~{}\mu{}^{-1}} along the axis.
C.4 Simulating the outboard model
Once the flow fields are known, we can simulate the dynamics of tracer particles under the assumption of straight swimming by the microorganism. This approach is in the spirit of recent work by Shum and Yeomans Shum and Yeomans (2017).
For each tracer size, r_{\textmd{\tiny{P}}}=10^{-2+3(i-1)/(8-1)}\nobreak\mbox{~{}\mum} for CR and OM and r_{\textmd{\tiny{P}}}=10^{-2+2(i-1)/(8-1)}\nobreak\mbox{~{}\mum} for EC, where , simulations are performed with an ensemble of particles that do not interact with each other. Tracers are advected by the swimmer-generated velocity field with a velocity given by the Faxén relation,
[TABLE]
Particles experience steric interactions with the swimmer through a hard-core repulsion. We tried various prescriptions of the repulsion potential, including the Weeks-Chandler-Anderson potential ( for small , with a cut-off radius ) as well as a softer potential (). To save computation time, it is also possible to set and if the particle overlaps with the swimmer after a timestep, in the co-moving frame, renormalise the distance to but keep the new polar angle . Supplementary Videos 9,10 (laboratory and co-moving frames respectively) at [url to be inserted] , show the tracers advected by the outboard CR in the deterministic regime.
Brownian motion is simulated with a standard Gaussian white noise , with a diffusion constant given by the Stokes-Einstein relation , where is the Boltzmann constant, is the temperature (not to be confused with the contact time ), and is the fluid viscosity.
Appendix D Contact time theory
This section develops a simple estimate for the contact time between a tracer particle of radius and a simplified ‘outboard’ swimmer. This section will then be complemented by a description of the full distribution of entrainment times in Appendix E. The swimmer is here simplified to a spherical body of radius and a single flagellum represented by one external Stokeslet oriented along the negative direction and located at a position with respect to the body centre (; for a puller; for a pusher). The force- and torque-free swimmer moves with a constant velocity along the positive axis, and we examine the motion of a tracer in the frame co-moving with the swimmer.
D.1 Flow close to the swimmer’s body
The swimmer-generated flow field is the sum of the body and flagellar flows: , and (see Appendix C.1). The body flow, Eq. C.1, can be obtained from the stream function
[TABLE]
This provides the streamlines for a given impact parameter :
[TABLE]
where the closest distance of approach is given by at the polar angle ; as well as the flow field
[TABLE]
where . Figures 11,12 show that both expressions are valid close to the swimmer’s body. Note that this is a pusher-type swimmer, but the same derivation holds for pullers. Moreover, Fig. 11b) shows that the functional shape in Eq. 30 is also a good estimate for the flagellar streamlines close to the swimmer body. The flagellar flow can be expanded in this region as
[TABLE]
The flow field approximations Eq. 31,32 are shown in Fig. 12 with dashed lines, compared to the exact flows with solid lines, at the swimmer’s equator . Note that both approximate flows satisfy the no-slip boundary condition, and grow linearly with close to the body. For , is of the same order of magnitude than , whereas in the limit , and we recover the body flow as that generated by a sphere dragged through the liquid.
Overall, the total tangential flow near the body in the co-moving frame can be written as
[TABLE]
For a more general flagellar orientation and position we still expect a similar functional form but with a more complex function , because the flagella always act to push or pull the liquid past the swimmer body faster, averaged over a swimming stroke.
D.2 Contact time without noise
Our experiments show that a particle is entrained further by an organism if it spends more time near its cell wall, in the ‘no-slip layer’. We compute the time taken for a particle to be advected along a stream line (Eq. 30) close to the swimmer
[TABLE]
where is the arclength differential along the stream line parameterised by the angle . Inserting Eq. 30 into 34, we find that the tangential flow along a streamline is constant to first order: For a given impact parameter we have
[TABLE]
where is the closest distance of approach. Therefore, taking the stream line length as the distance that a particle must travel around the swimmer, for small impact parameters, yields the contact time
[TABLE]
Note that in the limit of point-like tracer particles, , we recover the result by Mueller and Thiffeault Mueller and Thiffeault (2017): the entrainment length , where the constant for a bare no-slip sphere, as such that , and for typical swimmers. A particular feature of interest here are that the contact time, and hence the entrainment length, increases quadratically with the swimmer size . This implies there is a large difference between E. coli bacteria and Chlamydomonas algae.
Finite-sized particles do not have access to the stream lines very close to the swimmer body. Therefore, if the impact parameter is so small that , these particles collide with the front of the swimmer body. Lubrication forces and steric interactions expel them, so that they cross stream lines. Hence, in the co-moving frame, they approximately move along a circular trajectory around the body when and into the orbit of closest approach, the streamline with , at . As a result, the average contact time is reduced for large particles, because they cannot reach the no-slip layer close to the body and thus flow past the swimmer, as seen in its co-moving frame, more quickly.
Finally, we see that the solution diverges as with decreasing impact parameter. This can lead to very long entrainment events, like a ball pushed on the nose of a seal. However, this position is unstable with the introduction of thermal fluctuations, as we consider next.
D.3 Contact time with noise
We consider a Brownian particle advected in a linear shear flow over a straight solid surface that mimicks the swimmer’s cell wall (main text Fig. 4a). The flow velocity is , where the strain rate derives from the velocity along a streamline, using Eq. 37, so that
[TABLE]
A particle of radius is initially positioned at , disperses with diffusivity and is advected by the flow , but cannot cross the line . Without loss of generality Van Kampen (1983) this system is mapped to an ‘image’ system (main text Fig. 4b). Here, the particle is initially located at , the modified flow is , and the tracer can cross the surface. We aim to compute the average time needed for the colloid to travel a distance along the positive -direction. The stochastic equations of motion are
[TABLE]
where the noise correlations are defined as
[TABLE]
Note that the Faxén correction for finite-sized tracer particles need not be included here, as the Laplacian acting on pure shear flows vanishes. Integrating and averaging Eq. 41 gives
[TABLE]
Using the initial condition that particles start from , we can employ the canonical distribution to give
[TABLE]
Inserting this expression into Eq. 45 and integrating once more then yields
[TABLE]
Requiring that , we find the mean time is as the solution of the cubic equation
[TABLE]
which is solved using the Cardano formula. Only one positive and real root exists for all physical situations, and , which is the average contact time
[TABLE]
Hence, we can estimate the average entrainment length . This analytical expression can be evaluated for different tracer sizes, swimmer speed or size, temperature, fluid viscosity, etc. Note that the theory is expected to hold best near the optimal tracer size because the approximation in equations (30–52) holds best for particles that follow paths close to the body.
D.4 Streamline crossing
In the deterministic limit, , we recover Eq. 38 immediately from Eq. 48, in agreement with Mueller and Thiffeault Mueller and Thiffeault (2017). In this limit we do not observe a maximum in entrainment length or contact time, but a monotonic decrease with increasing particle size. This is because the smaller particles not diffuse away from small values and can access the streamlines closest to the no-slip surface, whereas larger particles cannot access this region due to steric interactions and experience therefore stronger tangential flows on average.
As a consequence, large particles with small impact parameters, i.e. , can therefore not stay in their original streamline, but must cross streamlines. They move around the swimmer body at distance and polar angles , and subsequently move along the streamline defined by at polar angles (as seen in main text Fig. 2c-d). During the first part of this trajectory, according to Eq. 34, these particles experience a tangential flow
[TABLE]
which has an explicit dependence, whereas the flow speed along a streamline (37) during the second part of the trajectory is approximately constant to first order. Hence, with limited diffusion, large particles might temporarily be ‘trapped’ in the region where . This effect is expected to increase the contact time, because next to the time required to flow around the body, one must add the (first-passage) time required to escape the initial low-flow region.
As a result, our simple theory underestimates the contact times observed in our simulations (see main text Fig. 3a). Whereas the shape of the curve and position of the maximum are captured well, we see a quantitative difference of a factor of near the optimal tracer size. This is expected, because the impact parameter in the stochastic model () is effectively equal to rather than zero in the simulations. Indeed, by considering impact parameters in the range instead of in our simulations, we retain the shape of the curve but the magnitude at the maximum is reduced (see main text Fig. 3b).
The current theory hinges on the simplicty of a constant flow speed along a stream line, which allows the stochastic model to be solved with an analytical expression in closed form. A more accurate approach should account for streamline crossing due to steric interactions, for example with space-dependent strain rate in Eq. 41,
[TABLE]
This non-linear stochastic model is rather complex to solve mathematically and we have not yet explored it in detail. However, a way to proceed is to take the spatial average,
[TABLE]
This gives a constant strain rate, so the model can be solved exactly. The resulting expression is depicted by the dashed lines in Fig. 13a. Indeed, this provides a better quantitative agreement with the outboard model simulations, especially for large particles that are subject to streamline crossing.
Appendix E Entrainment distribution theory
It is possible to derive an analytical estimate for the distribution of contact times (and therefore entrainment lengths) by approximating the problem as a first-passage time process for a 1D advection-diffusion system. This is analytically tractable, gives valuable insights, and provides very good quantitative predictions for the distribution of entrainment length (see Fig. 1f main text). We start by considering a 1D system where a Brownian particle of diffusivity is subject to a background drift (along the positive direction). The particle starts at and we are interested in the probability distribution of the first-passage time at a boundary where .
The distribution is known to be (see e.g. page 88 in ref. Redner (2001))
[TABLE]
If we now consider this particle as the tracer being entrained by the microorganism, the first passage time can be translated into an entrainment length (Eq. 1 main text). This leads to the following distribution of the entrainment lengths:
[TABLE]
where is the length that a particle travels around the swimmer, i.e. . Figures 15a,b and Fig. 1f show that the functional form in Eq. 57 provides a remarkable fit to all experimental entrainment length distributions, when and are kept as fitting parameters. This suggests that the entrainment process can be accurately understood as an effective 1D drift-diffusion process. The challenge is now to relate the effective parameters to the experimental system.
To this end, we represent the entrainment process through the 2D system described in Fig. 16 (see also Fig. 4a main text). A Brownian particle of radius diffuses with thermal diffusivity in the plane, above an impenetrable wall at ; and it is subjected to a uniform background velocity , with strain rate . A particle that starts at will drift with an ensemble-averaged velocity which, after the time to cross the length (Eq. 50), is given by
[TABLE]
where is the probability of finding the particle at a distance from the bottom wall at time . The fitted values of can therefore be converted into experimental estimates for , and are plotted in Fig. 15c as black circles. Notice the minimum in the experimental values of , which corresponds to the optimal tracer size for entrainment. At the same time, the function is well known and therefore we can estimate as
[TABLE]
which leads to the solid black line in Fig. 15c when using the experimental CR parameters , , (value for the outboard CR), and . While quantitatively the expression Eq. 61 underestimates the experimental values by m, it nevertheless recovers very well the evolution with tracer size . In particular, the minima in both cases appear at the same , and therefore Eq. 61 provides a good estimate for the optimal particle size for entrainment.
The parameter in Eq. 57 can be interpreted as the effective diffusivity of the particles along the velocity direction (in the 2D process, Fig. 4a and b). We expect this quantity to be enhanced compared to thermal diffusivity because of the background shear flow, as originally realised by Taylor for molecular diffusion within a pipe. Adapting the derivation in James and Chrysikopoulos (2003) to the case of a uniform shear flow within a thickness , it is easy to show that the Brownian particles have an effective diffusivity along the -axis given by
[TABLE]
where . The fitted experimental values of are shown in Fig. 15c as red circles. The length scale has been introduced in order to reduce the 2D system into an effective 1D process, and in terms of the entrainment process, it can be interpreted as the transverse length scale the beads explore before reaching the end of the body at . We therefore estimate it as the sum of the average position over the surface and an excess due to fluctuations, given by the square root of the variance of the distribution:
[TABLE]
evaluated at the mean contact time . This can be estimated analytically, and for initial condition one obtains (see Eq. 46)
[TABLE]
This estimate is shown as a solid red line in Fig. 15c: it underestimates the fitted value of , but captures well the qualitative dependence on tracer size. The estimates in Eq. 61 and Eq. 64 could be improved by generalising Eq. 47 for an arbitrary initial position, and then averaging over all impact parameters, . However, the results are not analytically tractable and therefore loose the simplicity of the minimal-model approach we focus on here, which already provides a remarkable semi-quantitative description of the dynamics.
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