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Individuals & Modeling Microbial Populations: Examples & Challenges

This talk explores the challenges of modeling microbial populations and introduces individual-based modeling as a potential solution. It discusses the scales at which population theory holds and the problem of subgrid scale processes. The talk also highlights the importance of understanding individual dynamics in population systems.

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Individuals & Modeling Microbial Populations: Examples & Challenges

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  1. Individuals & Modeling Microbial Populations: Examples & Challenges Dave Siegel UC Santa Barbara

  2. Art by Farooq Azam

  3. Each microbe is an individual • Responds to its immediate surroundings • Can alter its local surroundings through its actions • Influence its neighbors by the transmission of its effects through the fluid media, by eating them or by being eaten

  4. Microbes make up populations… • Populations are assemblages of individual microbes • Population dynamics is the result of many individual interactions as modified by the fluid environment surrounding them • It is a population’s trajectory in time that we want / need to know… Need to make microbial population forecasts

  5. Microbial population forecasts • Need to know for policy seting… • Biogeochemical cycling of C, N, P, S, etc. • Occurrence of harmful algal blooms & hypoxia conditions • Transfer of NPP energy to higher trophic levels • Hopefully make these forecasts accurately • How do we use our understanding of individuals to forecast microbial populations?

  6. Microbial population forecasts • Population dynamics gives us the classic set of tools for making forecasts • However, present techniques are limited • Simple “box” models (PZN, PZND, PZNDB, …) • Functional group approaches are promising • The “art of modeling” is how biological detail is stuffed into each “box”

  7. Communities as collectives… • Microbial communities are the result of the collective interactions of many individuals (as modified by the fluid environment) • How do these collective enterprises work? • How do we account for individual dynamics in a population system?

  8. Outline of talk • Discuss modeling individuals & populations • Assess scales where population theory holds • Introduce the microbial subgrid scale problem • Give example where subgrid scale processes have population level consequences • Introduce an individual based model and the problems it introduces • Suggest some future directions…

  9. Microbial processes • Individual scale processes • Resource uptake & capture • Resource utilization • Reproduction • Other interspecific interactions (virulence, etc.) • Population scale processes • Competition • Predation • Other interspecific interactions (…)

  10. Modeling individuals Model individuals as discrete entities • Need to know ID & state for each individual State vector: ai(type; x, u, Qj; t) for all i & Sj(x,t) • Develop rules to predict future state of each individual & its interactions with its environs Transition rule: Dai(…) = f(ai(…),Sj(x,t), Dt) & DSj(…) = f(Sj(x,t), ai(…),…, aN(…), Dt) • Individual based modeling (IBM)

  11. Modeling populations Model populations as continuous fields • Define a population over a scale & report in units of [# / volume (or “BGC $”/volume)] • Develop rules to predict the future state for each population & resource in the system DPi(x,t) = f(type; P1(x,t), …, PM(x,t), S1(x,t), …) • Population dynamic modeling

  12. What is the size of that volume? • Populations are continuous fields • Minimum scale of investigation must large enough to insure stable estimates of P(x,t) • Need to “count” large number of organisms • If N = 400 => Parcel scale, Lp ~ 7 P-1/3 For P = 106 ml-1 => Lp ~ 0.7 mm ~ 700 mm For P = 1 ml-1 => Lp ~ 70 mm ~ 70,000 mm • Only consider scales > Lp Siegel [1998] L&O, 43, 1133

  13. What does the flow do? Smallest relevant flow scale is the Batchelor scale, LB = [D2n / e]1/4 Balance between fluid stretching & molecular diffusion on solute distribution LB for nitrate in seawater range from 10-200 mm depending on e (D = 1.4x10-9 m2 s-1) For organic solutes, LB will be even smaller And organisms can make this even smaller…

  14. Are microbes populations? • We find that LB << Lp Flow length scales are << parcel scales Lp S(x,t) LB This does not count yet smaller solute scales imposed by individuals

  15. Are microbes populations? • Turbulence creates solute variations on scales smaller than Lp • Violates the fluid continuum hypothesis => populations are not chemical species • Within a “population parcel” there will be fluctuations in substrate levels • Marine microbes are discrete populations

  16. Dynamics of discrete populations • Microbes are spaced too far apart compared with variations in solute distributions • The speed at which neighboring individuals interact is important • If fast, then discreteness may not matter • If slow, then it may be critical • Important for understanding the role of individuals in competition, predation, etc. Siegel [1998] L&O, 43, 1133

  17. How do we now model microbes? • Assume microbes are populations and fit parameter values to data • These parameters are uptake kinetics, mortality rate, etc. • Unfortunately, these are parameterizations for both biological process & discreteness • A microbial subgrid scale (SGS) problem…

  18. Microbial SGS problems • How do processes on unresolved scales affect resolved scale processes? • In flows, small scale motions “influence” large scale motions (turbulent diffusion) • This is called a subgrid scale (SGS) problem • Leads to eddy diffusivities & closure models • A mircobial SGS model is the link between discrete & population-level descriptions

  19. Example of a microbial SGS problem

  20. A simple example • Illustrate role of individual scale process on population level dynamics • Resource competition among microbes • Molecular diffusivity as control parameter • Increasing diffusivity increases speed at which individuals interact & vice versa • Does the “winner” of this competition change?

  21. Microbial resource competition • A community of N different “species” • All require substrate (S) though each “species” is slightly different (10%) • Uptake follows Michaelis-Menten kinetics • Mortality is first order • Nearly all of their internal S concentration is instantaneously remineralized (fi = 0.99)

  22. Microbial resource competition Ci = concentration of nutrient in species i [mM] Ci = Ni * Qi = (abundance) * (cellular S) Vi = max uptake rate [d-1], Ki = ½ sat coef [mM], mi = mortality [d-1], fi = remineralization fraction

  23. Uptake [d-1] Substrate [mM] Microbial resource competition • Parameters (Vm,i, Ki, mi, Ri) vary 10% from mean • Mean [Vm,i Ki mi Ri] = [3 d-1 0.2 mM 2 d-1 0.4 mm] • fi = 0.99 (remin frac) • S(t=0) = 1 mM • SCi = 1 mM – log normal species list (N=25) • Well mixed assumption S(x,t) = f(t) only

  24. Winner is species 13!! Microbial resource competition Abundance Log10(Abundance)

  25. Microbial resource competition Substrate Log10(Substrate) SCi S Srefract

  26. Microbial resource competition Abundance Log10(Abundance)

  27. Microbial assemblageamendmentexperiments • Filtered Sargasso Sea water + amendment • Same DOC added • FISH probes for bacterial lineages Craig Carlson– unpubl.

  28. Diffusive “limitation” • Osmotrophs acquire resources across their cell wall • Rates of solute diffusion in water are very slow • Molecular diffusivities vary 1x10-11 to 1x10-7 m2 s-1 • At steady state, a balance between nutrient uptake and diffusion within its “boundary layer” is found S(r) S∞ Scell Diffusion Munk & Riley [1952] Pasciak & Gavis [1974] Nutrient Deficit

  29. Diffusive “limitation” • Nutrient transport can be modeled with Fick’s law • At steady state, nutrient transport across different spherical “shells” surrounding the cell is constant

  30. Diffusive “limitation” • Diffusive transport at cell wall is then • At steady state, this balances nutrient assimilation

  31. Diffusive “limitation” • Solve for Scell as f(uptake, diffusivity, geometry) • Facts about diffusive limitation Scell < S∞ => V(Scell) < V(S∞) (S∞ - Scell) increases as Q & Vmax get larger (S∞ - Scell) increases as D & Rcell get smaller

  32. Diffusion & resource competition Same parameters modulo the addition of size & cell quota Siegel and Brzezinski, to be published someday … maybe …

  33. Diffusion & resource competition Abundance Log10(Abundance)

  34. No diffusion case!! Abundance Log10(Abundance)

  35. Diffusion & resource competition Abundance Log10(Abundance) S Srefract SCi • Substrate uptake is strongly reduced by diffusion limitation

  36. Winner is now species 10!! It was species 13… Diffusion & resource competition Abundance Log10(Abundance)

  37. Results of simple example • Adding an individual-scale process (diffusive limitation) alters the population-scale results • Only difference among species was cell size - yet a new “winner” emerged • Diffusive limited uptake altered time courses of stock changes & nutrient drawdown • Different substrates can have different diffusivities allowing for yet different outcomes

  38. But… • Each organism still saw the same substrate concentration - not close to Farooq’s cartoon We need to… • Understand microbial geography • Represent critical parts of organism life cycle • Allow organisms to interact with their local environ & with each other

  39. Individual Based Modeling (IBM) • Develop a spatial, discrete world Account for the organism life cycle Include fluid environment connecting organisms but with much unoccupied regions to mimic the discrete ocean Contain enough organisms so experiment works Compare to a population-level dynamical model • Example – Two diatoms competing for SiO4

  40. An IBM of diatom competition Af Su • Discrete analog of the chemostat equations • Solve in 3D for 1 ml • High spatial resolution (100x100x100; Dx=100 mm) • Model the cell’s life cycle • Interaction by molecular diffusion of SiO4 only • Compare discrete results with chemostat equations Langston, Siegel & Brzezinski [to remain unpublished]

  41. Computational life cycle Cells divide when their quotas are twice a minimum Cells assimilate local nutrients Cells can move by sinking or swimming Daughter cells are located randomly Death occurs randomly Nutrients diffuse by Fick’s law Dead cell nutrients are recycled locally

  42. Example slice through domain Su Af

  43. Example slice through domain Su

  44. SiO4 Su Af Role of diffusion IBM Population Dynamics IBM results match analytical theory… On average, cells see ~Scell not something else

  45. We have a nested SGS problems • Microbial discreteness needs to be accounted for on the scale of a population – SGS1 Unresolved interactions among individuals affects population level change This is what I have been focused on • Solution to SGS1… Need to compare IBM results to population level models – construct ad hoc closures Key are spatial moments of population covariances

  46. Size matters – SGS2 • Microbe sizes vary from 0.1 to >100 mm, but grid scale (Dx) is 100 mm • Can’t make Dx thatmuch smaller (computers are only so big…) • Need to correctly account for the effects that an individual imposes on its environment • Local models are required to “merge” individuals into the environment

  47. Diversity Matters – SGS3 • How can we model viruses & diatoms? Nvirus ~ 107 ml-1 & Ndia ~ 10 ml-1 Lp for viruses ~ 20 mm & Lp for diatoms ~ 3 cm Implies number of model grids > 104 on a side Not good, but remember Moore’s Law • This is a very hard (& good) problem (Though I think we can put it off for a bit)

  48. Points I tried to make • Microbes are individuals & it matters • Alters interactions rates among individuals • Makes population models case specific • Resolution of this issue requires solution of the “microbial subgrid scale” problems • Provide a path for modeling microbial dynamics from “first principles”

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