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Bacteria push the limits of chemotactic precision to navigate dynamic chemical gradients
Edited by Howard C. Berg, Harvard University, Cambridge, MA, and approved April 15, 2019 (received for review September 26, 2018)

Significance
The limited precision of sensory organs places fundamental constraints on organismal performance. An open question, however, is whether organisms are routinely pushed to these limits and how limits might influence interactions between populations of organisms and their environment. By combining a method to generate dynamic, replicable resource landscapes, high-speed tracking of freely moving bacteria, a mathematical theory, and agent-based simulations, we show that sensory noise ultimately limits when and where bacteria can detect and climb chemical gradients. Our results suggest that the typical chemical landscapes bacteria inhabit are dominated by noise that masks shallow gradients and that the spatiotemporal dynamics of bacterial aggregations can be predicted by mapping the region where gradient signal rises above noise.
Abstract
Ephemeral aggregations of bacteria are ubiquitous in the environment, where they serve as hotbeds of metabolic activity, nutrient cycling, and horizontal gene transfer. In many cases, these regions of high bacterial concentration are thought to form when motile cells use chemotaxis to navigate to chemical hotspots. However, what governs the dynamics of bacterial aggregations is unclear. Here, we use an experimental platform to create realistic submillimeter-scale nutrient pulses with controlled nutrient concentrations. By combining experiments, mathematical theory, and agent-based simulations, we show that individual Vibrio ordalii bacteria begin chemotaxis toward hotspots of dissolved organic matter (DOM) when the magnitude of the chemical gradient rises sufficiently far above the sensory noise that is generated by stochastic encounters with chemoattractant molecules. Each DOM hotspot is surrounded by a dynamic ring of chemotaxing cells, which congregate in regions of high DOM concentration before dispersing as DOM diffuses and gradients become too noisy for cells to respond to. We demonstrate that V. ordalii operates close to the theoretical limits on chemotactic precision. Numerical simulations of chemotactic bacteria, in which molecule counting noise is explicitly taken into account, point at a tradeoff between nutrient acquisition and the cost of chemotactic precision. More generally, our results illustrate how limits on sensory precision can be used to understand the location, spatial extent, and lifespan of bacterial behavioral responses in ecologically relevant environments.
Motile bacteria often survive by consuming ephemeral sources of dissolved organic matter (DOM) produced, for example, in the ocean by phytoplankton lysis and exudation or sloppy feeding and excretion by larger organisms (1⇓⇓–4). The microscale interactions between nutrient sources and bacteria underpin ocean biogeochemistry and are strongly influenced by the ability of bacteria to actively navigate toward favorable conditions. Past experiments on chemotaxis using Escherichia coli and other model bacteria have generally focused on stable gradients of intermediate to high nutrient concentrations, where bacteria can readily detect chemical gradients (5⇓–7). However, the environments that wild bacteria navigate are often characterized by short-lived, microscale chemical gradients where background conditions are highly dilute (8, 9). In such ephemeral chemical fields, bacteria experience a gradient in DOM concentration as a noisy, dynamic signal, rather than as a steady concentration ramp (10).
Chemotactic bacteria rely on temporal gradient sensing to bias their swimming behavior according to whether their measurement of a chemical concentration is rising or falling over time. Such measurements are accomplished by using sophisticated receptors on their surface, combined with intracellular transduction pathways (11). This process fundamentally involves interaction with discrete chemoattractant molecules (12): Intrinsic randomness in the encounter rate affects a cell’s measurement of the gradient. This randomness places fundamental constraints on the cell’s ability to resolve gradients.
Theoretically, the relationship between the magnitude of a gradient signal and the noise associated with a cell’s measurement of that signal—the signal-to-noise ratio (SNR)—determines when and where cells can perform chemotaxis. Recent theoretical work has explored the physical limits on the accuracy and precision of cellular gradient sensing (13, 14), expanding on the seminal work of Berg and Purcell (12).
In natural environments, gradients are often noisy, in part due to low concentrations and local fluctuations, and can change over timescales comparable to the chemotactic response (15⇓–17). Understanding what governs chemotaxis and aggregation of bacteria in these noisy, ephemeral environments requires coupling an experimental method for precisely quantifying bacterial responses to microscale nutrient pulses, with a theoretical framework that specifically incorporates sensory noise. This has so far remained elusive.
Quantifying Chemotaxis in Realistic Microenvironments
To create controlled, dynamic nutrient pulses that mimic those that bacteria interact with in the ocean, we developed a system to introduce and make almost instantly available to the bacteria an amino acid source with known concentration into a chemically dilute background within a microfluidic chamber (18) (SI Appendix). Before the experiment, the chamber was filled with a known concentration of 4-methoxy-7-nitroindolinyl-caged-L-glutamate, a “caged” version of the amino acid glutamate—a potent chemoattractant and one of the most abundant dissolved amino acids in coastal waters (19). When bound to the cage, glutamate was undetectable by the bacteria. By exposing the center of the chamber to a focused LED pulse, a controlled quantity of glutamate was photoreleased (20, 21) in a vertical column (Fig. 1A). The amount of glutamate can be controlled to match the amino acids released from a lysing phytoplankton cell (2). In the experiments, this was varied in the range 0.0088–0.22 pmol, where the number of molecules released in the pulse can be determined by a calibration relationship between exposure time and uncaging fraction (Fig. 3 and SI Appendix, Fig. S4). The subsequent diffusion of this axisymmetric cylindrical pulse (diffusivity DC = 608 μm2⋅s−1) is well-approximated by a point source spreading with a Gaussian profile
Bacteria are able to perform chemotaxis in the presence of molecule counting noise. (A) Localized chemoattractant becomes available at the center of the chamber through photorelease of caged glutamate (orange), which subsequently diffuses and attracts chemotactic bacteria (blue). (B) Bacterial trajectories are extracted across the domain, revealing runs (white), reversals (red), and flicks (green). (C) The discrete nature of glutamate encounters introduces noise into the bacterium’s gradient measurement on top of other sources of noise. (D) Contours showing the instantaneous rate of encounter with glutamate molecules experienced by bacteria (shown at
To measure how cells respond to this rarefied chemical pulse (Fig. 1D), we recorded >1 million bacterial trajectories (Fig. 1B) over 20 min starting at pulse release for three replicate pulses. This allowed us to measure motion at the single-cell level and to quantify chemotactic behavior at the population level. For each track (Fig. 2A), we quantified the angle, θ, between the cell’s instantaneous swimming velocity and the vector pointing from the cell position to the center of the pulse (Fig. 2C). At
Bacterial drift is confined to discrete regions in space and time where the SNR is sufficiently high. (A) Single-cell trajectories in the first 60 s following pulse release. (B) Schematic of the mean glutamate concentration as a function of the distance from the center of a pulse. Far from and near to the pulse center, the SNR is low. At an intermediate distance, concentration gradients are strong, and the gradient signal can emerge above noise. (C) The swimming velocity of each bacterium makes an angle θ relative to the radial vector toward the pulse center. (D) Probability distribution,
Measurement Noise and Bacterial Chemotaxis
Small motile cells in the size range of E. coli, sperm cells (22), many Vibrios, and other bacteria cope with high levels of noise when estimating the concentrations and gradients of chemicals (14, 16). Over some short time interval
Eq. 1 illustrates that the uncertainty in the gradient measurement depends on the local chemical concentration,
Linking Measurement Noise and Chemotactic Performance
To determine whether and how measurement noise affected the chemotactic response of bacteria in our experiments, we developed a simplified model of the Vibrio chemotaxis response that incorporated the essential features of bacterial navigation. Many details of the chemotaxis pathway that are known for E. coli (23⇓–25) are not known for Vibrio ordalii, nor are such details known for most nonmodel bacteria. We therefore modeled Vibrio chemotaxis using a minimal model inspired by Long et al. (26) to combine the physical theory of Eq. 1 with the essential features of gradient measurement, adaptation, and motor output. For each bacterium, we model an internal state variable,
Eq. 2 involves two distinct timescales: the adaptation timescale
V. ordalii exhibits run–reverse–flick locomotion (Fig. 1B). We simulated its chemotactic behavior by modeling transitions from run to reverse and from reverse to flick, assuming the associated switching rates to be governed by a nonhomogeneous Poisson process with rate
Predicting Chemotactic Performance of a Population
Using the above model of chemotaxis, we performed 3D agent-based simulations of populations of bacteria foraging in the dynamic nutrient landscape studied in our experiments. Cells were subject to rotational diffusion and executed run–reverse–flick motion (Fig. 1 B, Inset) with reorientation angles drawn from distributions for a closely related Vibrio species (29) (SI Appendix). The agent-based model was compared with experimental data by fitting the precision factor Π, the motor gain Γ, and the rescaled receptor gain κ to data on the radial drift velocity of bacteria from our experiment (SI Appendix). The results depend more strongly on the precision factor than on either of the gains (SI Appendix, Fig. S6). The spatiotemporal evolution of the drift velocity from our experiments (Fig. 3A) was captured by the computational model (Fig. 3B), with the formation of an expanding—and eventually disappearing—annular region of chemotaxing cells. Outside this dynamic annulus, the shallow gradients are masked by noise (Fig. 2B) and bacterial motion is unbiased. These results involving drift velocity are not to be confused with the previously reported “volcano effect” in bacterial density (30).
Simulations and theory which each incorporate molecule counting noise successfully predict zones of chemotaxis across various pulse sizes. (A) Experimentally measured radial drift velocity as a function of time and distance from the pulse, for initial pulses of concentration
The agreement between model and data was good across nutrient pulses of different intensities. We performed additional experiments in which we decreased the concentration of uncaged glutamate in the pulse by a factor of 5 and a factor of 25 (corresponding to
The observed value of
It will be important in future studies of the chemotaxis network to determine precisely the biochemical processes that set T. However, based on the timescale set by the phosphorylation and dephosphorylation cycle of CheY in E. coli (34), we expect the value of T to be very close to 0.1 s. Although the estimated value of the precision factor, Π, depends on the value of T, the dependence is not as strong as it might appear from Eq. 1. For example, setting
Continuum Theory
In addition to the computational model described, we developed a simplified continuum model to predict the chemotactic drift velocity, which incorporated gradient signal and measurement noise over a single run–reverse cycle (SI Appendix). Consider a cell that makes a run with speed v up a (locally) linear gradient, then reverses its direction. The durations of the forward and backward runs are determined by the cell’s measurement of the gradient, rather than the gradient’s true value. The values of the discrete gradient measurements,
Chemotactic Precision Governs Nutrient Uptake
To investigate the influence of measurement noise on the nutrient exposure across the bacterial population, we used the computational model to analyze the uptake dynamics for different values of Π. In doing so, we identified ecological tradeoffs that may give rise to the specific precision factor, Π, exhibited by V. ordalii. We characterized the potential uptake for each bacterium with position
(A–C) Numerical simulations of bacteria for varying values of the chemotactic precision factor (
Fig. 4D demonstrates that the time-dependent population-averaged uptake, U, depends strongly on the chemotactic precision factor, Π. Within ∼100 s following pulse release, the value of U peaks and then slowly declines. When considering the time-averaged potential uptake (over 300 s) as a function of Π, for different quintiles of the bacterial population, we find that the nutrient exposure for cells in the top 20% (in terms of the time-averaged potential uptake) is unaffected by changes in Π, for
Bacteria with a precision factor on the order of that observed experimentally (
It is instructive to consider the relative advantage attained by chemotactic cells compared with nonchemotactic “mutants,” which represent the limiting case where no gradients are detectable. The number of moles of glutamate released in the pulse is given by
DOM Hotspots as Ecological Units
These results allow us to quantify the spatial extent and lifespan of bacterial aggregations in realistic environments. One example is phycospheres in the ocean, the regions surrounding individual phytoplankton cells that are rich in DOM (9, 36). The continuum theory predicts a short period of active bacterial recruitment via chemotaxis (Fig. 5A), followed by many minutes of random motility-induced motion with
Time-dependent bacterial response to photoreleased nutrients of initial concentration
Discussion and Conclusions
Bacteria in the ocean encounter nutrient pulses from a range of sources. Our experimental system is designed to mimic a range of unsteady nutrient sources, such as the diffusive spreading of a plume behind a sedimenting particle (40), a nutrient filament produced by turbulent mixing (17), or the spreading source from a lysing phytoplankton cell (9, 41). Through experiment, theory, and numerical simulations, we have shown that the chemotactic motion of cells toward an unsteady nutrient source can only occur in discrete zones where the gradient signal is not obscured by noise. Importantly, our results demonstrate that there is a clear and predictable delineation between zones where chemotaxis can occur and those where it cannot.
For many real nutrient sources, the stochasticity in the chemoattractant is essential in understanding the chemotactic footprint. However, in many existing models for chemotaxis, it is assumed that cells are able to perfectly measure changes in their surrounding chemical concentration. This deterministic sensing is equivalent to setting
Is it surprising that V. ordalii operates so close to the limit of sensory precision? On one hand, it is intuitive that more precise sensing should facilitate better responses to the environment, and so natural selection should lead to bacteria capable of making precise measurements of the gradient. There is only a marginal difference between the nutrient exposure for cells with the sensory precision of V. ordalii, compared with cells with the theoretical optimum sensory precision (Fig. 4). However, sensory precision comes at a high cost (43). Suppressing internal noise in biochemical networks, for example, generally requires that a cell produce and maintain a greatly increased number of signaling molecules (34, 44), implying that cells must trade off the costs and benefits of noise suppression. Two potential ways for a cell to increase its chemotaxis performance are (i) by increasing swimming speed (16), which comes at the cost of devoting more energy to locomotion (45); and (ii) by increasing its chemotactic precision (i.e., decreasing Π), which comes at the cost of tighter regulation of noise in the signal transduction pathway (34, 44). Although we cannot here quantify the costs of noise suppression in the chemotaxis pathway, the plateaus in Fig. 4E for
We note that noise in the chemotaxis pathway, however, does not always degrade the ability of cells to climb gradients. In contrast with our result on the negative effect of (upstream) counting noise on chemotactic performance, recent studies with E. coli (46⇓–48) demonstrated that (downstream) signaling noise plays an important role in coordinating multiple motors (49) and can increase chemotactic sensitivity. Rigorous calculations in such model species where the chemotaxis pathway is better established may help shed light on the importance of correlations in measurement noise, out-of-equilibrium dynamics, and simultaneous contribution of multiple noise sources.
We have shown that sensory noise places fundamental constraints on the chemotactic abilities of cells and governs the density, spatial extent, and lifespan of bacterial aggregations. The timescale for initial recruitment through chemotaxis (tens of seconds) is much shorter than the lifetime of the bacterial aggregation (tens of minutes). This further highlights the ecological significance of chemotactic navigation during the initial seconds following the occurrence of a pulse, and therefore the crucial role of noise suppression.
From a modeling perspective, the ability to partition complex nutrient landscapes into discrete zones of active chemotaxis will facilitate the conceptual scaling up from single hotspots to larger domains of an ecosystem, such as the intricate turbulence-induced network of DOM in the ocean. Beyond marine bacteria, the approach of studying chemotactic zones with respect to the underlying gradient SNR is expected to find great utility in assessing the performance of other microbes, which have evolved in chemical microenvironments with fundamentally different spatiotemporal properties.
Materials and Methods
A detailed discussion of the experimental protocols, mathematical theory, and numerical simulations is included in the SI Appendix.
Acknowledgments
We thank V. Sourjik, N. Wingreen, T. Emonet, F. Menolascina, K. Son, V. Fernandez, and J. Keegstra for useful discussions. This work was supported by an Australian Research Council Discovery Early Career Researcher Award DE180100911 (to D.R.B.); The University of Melbourne Computational Biology Research Initiative and high-performance computing system (D.R.B.); a Swiss National Science Foundation Early Mobility Postdoctoral Fellowship (F.C.); a James S. McDonnell Foundation Fellowship (A.M.H.); Army Research Office Grants W911NG-11-1-0385 and W911NF-14-1-0431 (to S.A.L.); Simons Foundation Grant 395890 (to S.A.L.); Gordon and Betty Moore Marine Microbial Initiative Investigator Award GBMF3783 (to R.S.); and Simons Foundation Grant 542395 (to R.S.) as part of the Principles of Microbial Ecosystems Collaborative (PriME).
Footnotes
↵1D.R.B. and F.C. contributed equally to this work.
- ↵2To whom correspondence may be addressed. Email: d.brumley{at}unimelb.edu.au, carraraf{at}ethz.ch, or romanstocker{at}ethz.ch.
Author contributions: D.R.B., F.C., A.M.H., Y.Y., S.A.L., and R.S. designed research; D.R.B., F.C., and A.M.H. analyzed data; D.R.B., F.C., A.M.H., and R.S. wrote the paper; D.R.B. performed numerical simulations; D.R.B., F.C., and A.M.H. developed theory; and F.C. performed experiments.
The authors declare no conflict of interest.
This article is a PNAS Direct Submission.
This article contains supporting information online at www.pnas.org/lookup/suppl/doi:10.1073/pnas.1816621116/-/DCSupplemental.
Published under the PNAS license.
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