Abstract
Microbial communities are shaped by environmental metabolites, but the principles that govern whether different communities will converge or diverge in any given condition remain unknown, posing fundamental questions about the feasibility of microbiome engineering. Here we studied the longitudinal assembly dynamics of a set of natural microbial communities grown in laboratory conditions of increasing metabolic complexity. We found that different microbial communities tend to become similar to each other when grown in metabolically simple conditions, but they diverge in composition as the metabolic complexity of the environment increases, a phenomenon we refer to as the divergence-complexity effect. A comparative analysis of these communities revealed that this divergence is driven by community diversity and by the assortment of specialist taxa capable of degrading complex metabolites. An ecological model of community dynamics indicates that the hierarchical structure of metabolism itself, where complex molecules are enzymatically degraded into progressively simpler ones that then participate in cross-feeding between community members, is necessary and sufficient to recapitulate our experimental observations. In addition to helping understand the role of the environment in community assembly, the divergence-complexity effect can provide insight into which environments support multiple community states, enabling the search for desired ecosystem functions towards microbiome engineering applications.
This is a preview of subscription content, access via your institution
Access options
Access Nature and 54 other Nature Portfolio journals
Get Nature+, our best-value online-access subscription
$29.99 / 30 days
cancel any time
Subscribe to this journal
Receive 12 digital issues and online access to articles
$119.00 per year
only $9.92 per issue
Buy this article
- Purchase on SpringerLink
- Instant access to full article PDF
Prices may be subject to local taxes which are calculated during checkout
Similar content being viewed by others
Data availability
All raw 16S sequencing data and associated metadata generated for this study can be accessed with the NCBI BioProject accession PRJNA1074799 (https://www.ncbi.nlm.nih.gov/sra/PRJNA1074799). All processed data used in our analyses can be found on GitHub at https://github.com/segrelab/MetabolicComplexityDivergence. Source data are provided with this paper.
Code availability
All analysis and simulation code can be found on GitHub at https://github.com/segrelab/MetabolicComplexityDivergence.
References
Gilbert, J. A. et al. Current understanding of the human microbiome. Nat. Med. 24, 392–400 (2018).
Bowman, K. A., Broussard, E. K. & Surawicz, C. M. Fecal microbiota transplantation: current clinical efficacy and future prospects. Clin. Exp. Gastroenterol. 8, 285–291 (2015).
Averill, C. et al. Defending Earth’s terrestrial microbiome. Nat. Microbiol. 7, 1717–1725 (2022).
Jansson, J. K. & Hofmockel, K. S. Soil microbiomes and climate change. Nat. Rev. Microbiol. 18, 35–46 (2020).
Silverstein, M. R., Segrè, D. & Bhatnagar, J. M. Environmental microbiome engineering for the mitigation of climate change. Glob. Change Biol. https://doi.org/10.1111/gcb.16609 (2023).
Martiny, J. B. H. et al. Microbial biogeography: putting microorganisms on the map. Nat. Rev. Microbiol. 4, 102–112 (2006).
Martiny, J. B. H., Eisen, J. A., Penn, K., Allison, S. D. & Horner-Devine, M. C. Drivers of bacterial β-diversity depend on spatial scale. Proc. Natl Acad. Sci. USA 108, 7850–7854 (2011).
Goldford, J. E. et al. Emergent simplicity in microbial community assembly. Science 361, 469–474 (2018).
Pacheco, A. R., Osborne, M. L. & Segrè, D. Non-additive microbial community responses to environmental complexity. Nat. Commun. 12, 2365 (2021).
Enke, T. N. et al. Modular assembly of polysaccharide-degrading marine microbial communities. Curr. Biol. 29, 1528–1535.e6 (2019).
Bittleston, L. S., Gralka, M., Leventhal, G. E., Mizrahi, I. & Cordero, O. X. Context-dependent dynamics lead to the assembly of functionally distinct microbial communities. Nat. Commun. 11, 1440 (2020).
Čaušević, S., Tackmann, J., Sentchilo, V., von Mering, C. & van der Meer, J. R. Reproducible propagation of species-rich soil bacterial communities suggests robust underlying deterministic principles of community formation. mSystems 7, e00160–22 (2022).
Rivett, D. W. & Bell, T. Abundance determines the functional role of bacterial phylotypes in complex communities. Nat. Microbiol. 3, 767–772 (2018).
Datta, M. S., Sliwerska, E., Gore, J., Polz, M. F. & Cordero, O. X. Microbial interactions lead to rapid micro-scale successions on model marine particles. Nat. Commun. 7, 11965 (2016).
Estrela, S. et al. Functional attractors in microbial community assembly. Cell Syst. 13, 29–42.e7 (2022).
Grilli, J. Macroecological laws describe variation and diversity in microbial communities. Nat. Commun. 11, 4743 (2020).
Lawson, C. E. et al. Common principles and best practices for engineering microbiomes. Nat. Rev. Microbiol. 17, 725–741 (2019).
Dal Bello, M., Lee, H., Goyal, A. & Gore, J. Resource–diversity relationships in bacterial communities reflect the network structure of microbial metabolism. Nat. Ecol. Evol. 5, 1424–1434 (2021).
Marsland, R. et al. Available energy fluxes drive a transition in the diversity, stability, and functional structure of microbial communities. PLoS Comput. Biol. 15, e1006793 (2019).
Marsland, R., Cui, W. & Mehta, P. A minimal model for microbial biodiversity can reproduce experimentally observed ecological patterns. Sci. Rep. 10, 3308 (2020).
Marsland, R., Cui, W., Goldford, J. & Mehta, P. The Community Simulator: a Python package for microbial ecology. PLoS ONE 15, e0230430 (2020).
Gralka, M., Szabo, R., Stocker, R. & Cordero, O. X. Trophic interactions and the drivers of microbial community assembly. Curr. Biol. 30, R1176–R1188 (2020).
Thompson, L. R. et al. A communal catalogue reveals Earth’s multiscale microbial diversity. Nature 551, 457–463 (2017).
Sposito, G. The Chemistry of Soils (Oxford Univ. Press, 2016).
Atiwesh, G., Parrish, C. C., Banoub, J. & Le, T. T. Lignin degradation by microorganisms: a review. Biotechnol. Prog. 38, e3226 (2022).
Weng, C., Peng, X. & Han, Y. Depolymerization and conversion of lignin to value-added bioproducts by microbial and enzymatic catalysis. Biotechnol. Biofuels 14, 84 (2021).
Xu, Z., Lei, P., Zhai, R., Wen, Z. & Jin, M. Recent advances in lignin valorization with bacterial cultures: microorganisms, metabolic pathways and bio-products. Biotechnol. Biofuels 12, 32 (2019).
Iram, A., Berenjian, A. & Demirci, A. A review on the utilization of lignin as a fermentation substrate to produce lignin-modifying enzymes and other value-added products. Molecules 26, 2960 (2021).
Li, K. et al. Investigating lignin-derived monomers and oligomers in low-molecular-weight fractions separated from depolymerized black liquor retentate by membrane filtration. Molecules 26, 2887 (2021).
Gilkes, N. R., Kilburn, D. G., Miller, R. C. & Warren, R. A. J. Bacterial cellulases. Bioresour. Technol. 36, 21–35 (1991).
Bhardwaj, N., Kumar, B., Agrawal, K. & Verma, P. Current perspective on production and applications of microbial cellulases: a review. Bioresour. Bioprocess. 8, 95 (2021).
Jones, D. L. Organic acids in the rhizosphere—a critical review. Plant Soil 205, 25–44 (1998).
Fischer, Z., Blažka, P. & Dubis, L. Respiration rates of organic soil depending on changes of moisture and aeration. Open J. Soil Sci. 7, 101–110 (2017).
Ramonell, K. M. et al. Influence of atmospheric oxygen on leaf structure and starch deposition in Arabidopsis thaliana: low oxygen effects on leaf development in Arabidopsis. Plant Cell Environ. 24, 419–428 (2001).
Petersen, S. O., Nielsen, T. H., Frostegård, Å. & Olesen, T. O2 uptake, C metabolism and denitrification associated with manure hot-spots. Soil Biol. Biochem. 28, 341–349 (1996).
Sierra, J. & Renault, P. Oxygen consumption by soil microorganisms as affected by oxygen and carbon dioxide levels. Appl. Soil Ecol. 2, 175–184 (1995).
Parisutham, V., Chandran, S.-P., Mukhopadhyay, A., Lee, S. K. & Keasling, J. D. Intracellular cellobiose metabolism and its applications in lignocellulose-based biorefineries. Bioresour. Technol. 239, 496–506 (2017).
Blount, Z. D., Borland, C. Z. & Lenski, R. E. Historical contingency and the evolution of a key innovation in an experimental population of Escherichia coli. Proc. Natl Acad. Sci. USA 105, 7899–7906 (2008).
Ibarra, R. U., Edwards, J. S. & Palsson, B. O. Escherichia coli K-12 undergoes adaptive evolution to achieve in silico predicted optimal growth. Nature 420, 186–189 (2002).
Goyal, A., Bittleston, L. S., Leventhal, G. E., Lu, L. & Cordero, O. X. Interactions between strains govern the eco-evolutionary dynamics of microbial communities. eLife 11, e74987 (2022).
Dragosits, M. & Mattanovich, D. Adaptive laboratory evolution—principles and applications for biotechnology. Microb. Cell Fact. 12, 64 (2013).
Debray, R. et al. Priority effects in microbiome assembly. Nat. Rev. Microbiol. 20, 109–121 (2022).
Estrela, S., Sanchez-Gorostiaga, A., Vila, J. C. & Sanchez, A. Nutrient dominance governs the assembly of microbial communities in mixed nutrient environments. eLife 10, e65948 (2021).
Louca, S. et al. Function and functional redundancy in microbial systems. Nat. Ecol. Evol. 2, 936–943 (2018).
Allison, S. D. & Martiny, J. B. H. Resistance, resilience, and redundancy in microbial communities. Proc. Natl Acad. Sci. USA 105, 11512–11519 (2008).
Louca, S. et al. High taxonomic variability despite stable functional structure across microbial communities. Nat. Ecol. Evol. 1, 0015 (2017).
Dubinkina, V., Fridman, Y., Pandey, P. P. & Maslov, S. Multistability and regime shifts in microbial communities explained by competition for essential nutrients. eLife 8, e49720 (2019).
Johnson, D. R., Goldschmidt, F., Lilja, E. E. & Ackermann, M. Metabolic specialization and the assembly of microbial communities. ISME J. 6, 1985–1991 (2012).
Berlemont, R. & Martiny, A. C. Phylogenetic distribution of potential cellulases in bacteria. Appl. Environ. Microbiol. 79, 1545–1554 (2013).
Kost, C., Patil, K. R., Friedman, J., Garcia, S. L. & Ralser, M. Metabolic exchanges are ubiquitous in natural microbial communities. Nat. Microbiol. 8, 2244–2252 (2023).
Speck, E. L. & Freese, E. Control of metabolite secretion in Bacillus subtilis. J. Gen. Microbiol. 78, 261–275 (1973).
Hannya, A., Nishimura, T., Matsushita, I., Tsubota, J. & Kawata, Y. Efficient production and secretion of oxaloacetate from Halomonas sp. KM-1 under aerobic conditions. AMB Express 7, 209 (2017).
Beg, Q. K. et al. Detection of transcriptional triggers in the dynamics of microbial growth: application to the respiratorily versatile bacterium Shewanella oneidensis. Nucleic Acids Res. 40, 7132–7149 (2012).
Fernández-Veledo, S. & Vendrell, J. Gut microbiota-derived succinate: friend or foe in human metabolic diseases? Rev. Endocr. Metab. Disord. 20, 439–447 (2019).
Balado, M. et al. Secreted citrate serves as iron carrier for the marine pathogen Photobacterium damselae subsp damselae. Front. Cell. Infect. Microbiol. 7, 361 (2017).
Pacheco, A. R., Moel, M. & Segrè, D. Costless metabolic secretions as drivers of interspecies interactions in microbial ecosystems. Nat. Commun. 10, 103 (2019).
Tiedje, J., Sexstone, A., Parkin, T. & Revsbech, N. Anaerobic processes in soil. Plant Soil 76, 197–212 (1984).
Fritts, R. K., McCully, A. L. & McKinlay, J. B. Extracellular metabolism sets the table for microbial cross-feeding. Microbiol. Mol. Biol. Rev. 85, e00135–20 (2021).
Amarnath, K. et al. Stress-induced metabolic exchanges between complementary bacterial types underly a dynamic mechanism of inter-species stress resistance. Nat. Commun. 14, 3165 (2023).
Cui, W., Marsland, R. & Mehta, P. Diverse communities behave like typical random ecosystems. Phys. Rev. E 104, 034416 (2021).
Al-Ani, A. et al. Oxygenation in cell culture: critical parameters for reproducibility are routinely not reported. PLoS ONE 13, e0204269 (2018).
Rocca, J. D. et al. The microbiome stress project: toward a global meta-analysis of environmental stressors and their effects on microbial communities. Front. Microbiol. 9, 3272 (2019).
Mandakovic, D. et al. Structure and co-occurrence patterns in microbial communities under acute environmental stress reveal ecological factors fostering resilience. Sci. Rep. 8, 5875 (2018).
Dal Co, A., van Vliet, S., Kiviet, D. J., Schlegel, S. & Ackermann, M. Short-range interactions govern the dynamics and functions of microbial communities. Nat. Ecol. Evol. 4, 366–375 (2020).
Carthew, R. W. Gene regulation and cellular metabolism: an essential partnership. Trends Genet. 37, 389–400 (2021).
Ramin, K. I. & Allison, S. D. Bacterial tradeoffs in growth rate and extracellular enzymes. Front. Microbiol. 10, 2956 (2019).
Malik, A. A. et al. Defining trait-based microbial strategies with consequences for soil carbon cycling under climate change. ISME J. 14, 1–9 (2020).
Stokes, J. M., Lopatkin, A. J., Lobritz, M. A. & Collins, J. J. Bacterial metabolism and antibiotic efficacy. Cell Metab. 30, 251–259 (2019).
van den Berg, N. I. et al. Ecological modelling approaches for predicting emergent properties in microbial communities. Nat. Ecol. Evol. 6, 855–865 (2022).
Sánchez, Á. et al. Directed evolution of microbial communities. Annu. Rev. Biophys. 50, 323–341 (2021).
M9 minimal medium (modified). Cold Spring Harb. Protoc. pdb.rec12296 (2010).
Liu, J., Li, J., Feng, L., Cao, H. & Cui, Z. An improved method for extracting bacteria from soil for high molecular weight DNA recovery and BAC library construction. J. Microbiol. 48, 728–733 (2010).
Syuhada, N. H. et al. Strong and widespread cycloheximide resistance in Stichococcus-like eukaryotic algal taxa. Sci. Rep. 12, 1080 (2022).
Bolyen, E. et al. Reproducible, interactive, scalable and extensible microbiome data science using QIIME 2. Nat. Biotechnol. 37, 852–857 (2019).
Martin, M. Cutadapt removes adapter sequences from high-throughput sequencing reads. EMBnet J. 17, 10 (2011).
Callahan, B. J. et al. DADA2: high-resolution sample inference from Illumina amplicon data. Nat. Methods 13, 581–583 (2016).
Rognes, T., Flouri, T., Nichols, B., Quince, C. & Mahé, F. VSEARCH: a versatile open source tool for metagenomics. PeerJ 4, e2584 (2016).
Gloor, G. B., Macklaim, J. M., Pawlowsky-Glahn, V. & Egozcue, J. J. Microbiome datasets are compositional: and this is not optional. Front. Microbiol. 8, 2224 (2017).
Quinn, T. P., Erb, I., Richardson, M. F. & Crowley, T. M. Understanding sequencing data as compositions: an outlook and review. Bioinformatics 34, 2870–2878 (2018).
Pedregosa, F. et al. Scikit-learn: machine learning in Python. J. Mach. Learn. Res. 12, 2825–2830 (2011).
Acknowledgements
We thank M. Dal Bello, A. Goyal, M. Gralka, Z. Werbin, J. Zhang, K. Herbst, J. Goldford, H. Scott, S. Bald and the members of the Bhatnagar and Segrè labs for their guidance and insight. Additionally, we thank C. Vietorisz for assistance with soil community sampling. M.R.S. was supported by a synthetic biology NIH-funded predoctoral training fellowship (T32GM130546), a bioinformatics NIH-funded predoctoral training fellowship (T32GM100842), the Biological Design Center Kilachand Multicellular Design Program Graduate Fellowship and the Hariri Graduate Student Fellows Program. J.M.B. acknowledges support from DOE DE-SC0020403 and DOE DE-SC0012704. D.S. acknowledges support from the National Institutes of Health (National Institute of General Medical Sciences, award R01GM121950; National Institute on Aging, award number UH2AG064704), the US Department of Energy, Office of Science, Office of Biological & Environmental Research through the Microbial Community Analysis and Functional Evaluation in Soils SFA Program (m-CAFEs) under contract number DE-AC02-05CH11231 to Lawrence Berkeley National Laboratory, the National Science Foundation (grants 1457695, NSFOCE-BSF 1635070 and NSF-BSF 2246707; and the NSF Center for Chemical Currencies of a Microbial Planet, publication #044) and the Human Frontiers Science Program (RGP0020/2016 and RGP0060/2021). Figures were created with BioRender.com.
Author information
Authors and Affiliations
Contributions
M.R.S., J.M.B. and D.S. conceived the study. M.R.S. acquired samples, conducted the experiments, performed the simulations and analysed the data. M.R.S., J.M.B. and D.S. interpreted results and wrote the manuscript.
Corresponding author
Ethics declarations
Competing interests
The authors declare no competing interests.
Peer review
Peer review information
Nature Ecology & Evolution thanks Otto Cordero and the other, anonymous, reviewer(s) for their contribution to the peer review of this work. Peer reviewer reports are available.
Additional information
Publisher’s note Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
Extended data
Extended Data Fig. 1 Microbial communities stabilize.
Each point is the mean distance to a community’s previous timepoint within each condition and the shaded region represents the 95% confidence interval. On day 3, communities are substantially different from their initial state and then continue to change in composition, but by approximately the same amount.
Extended Data Fig. 2 Divergence of a subset of communities which are available for all days.
A reproduction of Fig. 1d–f, but excluding all samples from communities HF1P and HF3H, which are missing data for days 3, 6, and 9 (Extended Data Table 1). a, Divergence of communities within each condition over time from day 3 onwards. Points on each line represent the mean divergence and the shaded region represents the 95% confidence interval for pairwise distances between all four included communities within each condition. b, Distribution of divergence for the final time point. Boxes are bound by the interquartile range, divided by the median, and whiskers extend to a maximum of 1.5 times the interquartile range. c, Divergence-complexity effect by condition type for all time points (one-sided Wald Test on effect (slope) > 0, p-values shown in figure for each day and condition type.
Extended Data Fig. 3 Divergence-complexity effect at Family level.
A reproduction of divergence-complexity effect calculation in Fig. 2f except computing divergence at the Family level instead of at the ASV level (one-sided Wald Test on effect (slope) > 0, p-values shown in figure for each day and condition type). Unlike our results at the ASV level, the divergence-complexity effect for our mixed-metabolite conditions at the Family level was only significant for day 33. The lack of significance at other points may be related to their reduced sample size (for days 3, 6, and 9; see Extended Data Table 1), but may in principle reflect additional effects emerging upon taxonomic coarse graining.
Extended Data Fig. 4 Family composition over time.
Each subplot shows the Family composition over time for a microcosm. Colors for each Family are defined by Phylum where blue represents Actinobacteria, yellow represents Bacteroidetes, green represents Firmicutes, and red represents Proteobacteria. Each column of subplots pertains to one source community and each row pertains to a condition (increasing in complexity from top to bottom, with single- and then mixed-metabolite conditions).
Extended Data Fig. 5 Microcosm replicates cluster.
a, The final state at day 33 of two replicates for community HF1P and three replicates for all other communities (see Extended Data Table 1) projected separately for each condition using MDS. b, The distribution of distances across communities (N=1,066 pairwise distances) and between replicates within the same community (N=142 pairwise distances). Each violin outlines the kernel density estimate and contains a box which is bound by the interquartile range with an open circle at the media and whiskers that extend up to 1.5 times the interquartile range. Communities are colored by their source and squares represent the replicate used in the main text. Independent of condition, communities from the same replicate are more similar to each other than communities from separate replicates.
Extended Data Fig. 6 Divergence and diversity on a subset of communities which are available for all days.
A reproduction of Fig. 3, but excluding all samples from communities HF1P and HF3H, which are missing data for days 3, 6, and 9 (Extended Data Table 1). a, The slope of the relationship between community alpha diversity and divergence (black) and the mean community alpha diversity (red) over time. Shaded areas around each regression line represents the 95% confidence interval. b, The data underlying the relationship in a over time. Each point is the diversity of a community in a condition (x-axis) and the mean divergence of that community from all others within a condition (y-axis).
Extended Data Fig. 7 Consumer resource parameterizations.
D Matrices for trophic (a) and random (b) resource transformations. Each matrix column defines which resources are generated from a given input resource. a, Trophic resource transformations were parameterized by defining resource types (T0, T1, T2, and T3; red lines) which mostly transform into resources of the subsequent type with some self-renewal. b, Random resource transformations were parameterized by defining any resource to transform into any other resource with uniform probability. The colorbar indicates log10 resource transformation rate for a and b. C matrices for trophic (c) and random (d) consumer preferences. Each matrix row defines which resources can be utilized by each consumer. c, Trophic consumer preferences were parameterized by defining consumer families (F0, F1, F2, and G; blue lines) which consume a total of 35 resources of their associated type (for example, F0 consumers utilize T0 resources) and a common resource, T3. G consumers (generalists) consume resources of any type. d, Random consumer preferences were parameterized by defining consumers to utilize any resource with uniform probability. e, Seven initial environmental conditions were defined with 20 resources sampled from (1) T0, (2) T1, (3) T2, (4) T3, (5) T3+T2, (6) T3+T2+T1, and (7) T3+T2+T1+T0. f, Six source communities were defined by sampling 200 consumers.
Supplementary information
Supplementary Information
Supplementary text, Fig. 1 and Table 1.
Supplementary Data 1
Source data for Supplementary Fig. 1.
Source data
Source Data Fig. 1
Statistical source data.
Source Data Fig. 2
Statistical source data.
Source Data Fig. 3
Statistical source data.
Source Data Fig. 4
Statistical source data.
Source Data Fig. 5
Statistical source data.
Source Data Extended Data Fig. 1/Table 1
Statistical source data.
Source Data Extended Data Fig. 2/Table 2
Statistical source data.
Source Data Extended Data Fig. 3/Table 3
Statistical source data.
Source Data Extended Data Fig. 4/Table 4
Statistical source data.
Source Data Extended Data Fig. 5/Table 5
Statistical source data.
Source Data Extended Data Fig. 6/Table 6
Statistical source data.
Source Data Extended Data Fig. 7/Table 7
Statistical source data.
Rights and permissions
Springer Nature or its licensor (e.g. a society or other partner) holds exclusive rights to this article under a publishing agreement with the author(s) or other rightsholder(s); author self-archiving of the accepted manuscript version of this article is solely governed by the terms of such publishing agreement and applicable law.
About this article
Cite this article
Silverstein, M.R., Bhatnagar, J.M. & Segrè, D. Metabolic complexity drives divergence in microbial communities. Nat Ecol Evol 8, 1493–1504 (2024). https://doi.org/10.1038/s41559-024-02440-6
Received:
Accepted:
Published:
Issue Date:
DOI: https://doi.org/10.1038/s41559-024-02440-6