| Literature DB >> 27869702 |
Hans-Curt Flemming1,2,3.
Abstract
"Slime" played a brief and spectacular role in the 19th century founded by the theory of primordial slime by Ernst Haeckel. However, that substance was never found and eventually abandoned. Further scientific attention slowly began in the 1930s referring to slime as a microbial product and then was inspired by "How bacteria stick" by Costerton et al. in 1978, and the matrix material was considered to be polysaccharides. Later, it turned out that proteins, nucleic acids and lipids were major other constituents of the extracellular polymeric substances (EPS), an acronym which was highly discussed. The role of the EPS matrix turns out to be fundamental for biofilms, in terms of keeping cells in proximity and allowing for extended interaction, resource capture, mechanical strength and other properties, which emerge from the life of biofilm organisms, including enhanced tolerance to antimicrobials and other stress. The EPS components are extremely complex and dynamic and fulfil many functional roles, turning biofilms into the most ubiquitous and successful form of life on Earth.Entities:
Keywords: EPS; biofilms; emergent properties; nutrient acquisition; resistance; tolerance
Year: 2016 PMID: 27869702 PMCID: PMC5192524 DOI: 10.3390/microorganisms4040041
Source DB: PubMed Journal: Microorganisms ISSN: 2076-2607
Figure 1Bathybius Haeckelii. Figure 1 on Table 17 in Ernst Haeckels Article, Beiträge zur Plastidentheorie (1870) (Image in public domain).
Figure 2Resource caption and retention by and in biofilms. The biofilm is a sponge-like system that provides surfaces for the sorption of a diverse range of molecules that can be sequestered from the environment. This confers several benefits to the biofilm, such as nutrient acquisition and matrix stabilization. Similarly, the physicochemical properties of the matrix enable biofilms to retain and stabilize extracellular digestive enzymes produced by biofilm cells, turning the matrix into an external digestive system. Surface-attached biofilms are not only able to take up nutrients from the water phase but can also digest biodegradable components from the substratum, which is exposed to enzymes in the matrix (after [19], with permission).
Figure 3Fluorescent staining of a biofilm. Colour allocation: Nucleic acid stain (SybrGreen) = green; lectin stain (AAL-Alexa568) = red; autofluorescence of algae (chlorophyll A) = blue; autofluoresence of cyanobacteria = purple/white. Image dimensions: 246 × 246 μm (from [34], with permission, source: [35]).
Figure 4Properties of biofilms emerging from life in the EPS matrix (after [19], with permission).
Functions of extracellular polymeric substances (EPS) components (after [19], with permission).
| Function of EPS Component | Relevance for Biofilm Organism | EPS Components Involved |
|---|---|---|
| Adhesion | Initial steps in colonization of abiotic and biotic surfaces by planktonic cells, long-term attachment of whole biofilms to surfaces | Polysaccharides, proteins (e.g., fimbriae), eDNA |
| Aggregation of bacterial cells | Bridging between cells, (temporary) immobilization of bacterial populations, basis for development of high cell densities, cell-cell recognition | Polysaccharides, proteins, DNA |
| Cohesion of biofilms | Structural elements forming a hydrated polymer network (biofilm matrix), mediation of mechanical stability of biofilms (frequently in conjunction with multivalent cations or hydrophobic interactions), determination of EPS structure (capsule, slime, sheath) and biofilm architecture, generation of matrix | Neutral and charged polysaccharides, proteins (e.g., amyloids, lectins), DNA |
| Retention of water | Maintenance of highly hydrated microenvironment around biofilm organisms, dessication tolerance in water-deficient environments | Hydrophilic polysaccharides and Proteins; skin-forming hydrophobic proteins (BslA [ |
| Protective barrier against antimicrobials | Resistance to nonspecific and specific host defenses during infection, tolerance to various antimicrobial agents (e.g., disinfectants, antibiotics), protection of cyanobacterial nitrogenase from harmful effects of oxygen; protection against some (but not all!) grazers | Polysaccharides, proteins |
| Sorption of polar organic compounds | Accumulation of nutrients from the environment, sorption of xenobiotics (detoxification) | Charged or hydrophobic polysaccharides and proteins |
| Sorption of inorganic ions | Promotion of polysaccharide gel formation, ion exchange, mineral formation, accumulation of toxic metal ions (detoxification) | Charged polysaccharides and proteins, including inorganic substituents such as phosphate and sulphate |
| Sorption of apolar organic substances | Resource capture | Proteins, not yet defined hydrophobic pockets in matrix |
| Sorption of particles | Resource capture | Sticky matrix components |
| Enhanced access to resources captured in the matrix | Providing additional enzymatic competence and capacity in the matrix; killer-vesicles as a weapon in competition (Schooling and Beveridge [ | Membrane vesicles (contain nucleic acids, enzymes, proteins, LPS etc.) |
| Enzymatic activity | Digestion of exogenous macromolecules for nutrient acquisition, degradation of structural EPS allowing release of cells from biofilms, utilization of substratum as substrate | Proteins |
| Nutrient source | Source of C, N and P compounds for utilization by biofilm community | Potentially all EPS components |
| Genetic information | Horizontal gene transfer between biofilm cells | DNA |
| Intercellular information | Regulation of biofilm dynamics and responses, regulating c-di-GMP concentration | Polysaccharides |
| Electron donor or acceptor | Redox activity in biofilm matrix, electron transport mediation to surfaces | Proteins (e.g., pili, nanowires), humic substances |
| Resource capture by export of enzymes into matrix | Providing additional enzymatic competence and capacity in the matrix | Outer membrane vesicles (contain nucleic acids, enzyme proteins, lipopolysaccharides, phospholipids) |
| Sink for excess energy | Sink for excess carbon under unbalanced C:N metabolic conditions | Polysaccharides |
| Binding of enzymes | Accumulation, retention and stabilization of enzymes through their interaction with polysaccharides | Polysaccharides, enzyme proteins |
Overview of modification of EPS and matrix structure after excretion (after [48], with permission.
| Microbial Modification | Effect on EPS |
|---|---|
| Degradation of EPS components by hydrolases, esterases, lipases, proteases and other lytic enzymes | Shortening of chain length, degradation of EPS, change of matrix structure and stability, formation of pores and channels Destabilization of matrix, dispersion, release of biofilm organisms |
| Variation of EPS composition in mixed biofilms during development | EPS of different properties, resistance to EPS-lysing enzymes |
| Post-excretional addition of substituents to polysaccharides | Influence on shape, charge, hydrophobicity of polymer, surface activity |
| Molecular structure suitable for protein-polysaccharide interaction | Retention, possible protection and activation of extracellular enzymes |
| Excretion of rhamnolipids | Increase of porosity, favouring of cell motility, influencing mass transport |
| Movement of “stealth swimmers” Houry et al. [ | Formation of channels, improvement of convective mass transport |
| Environmental influence | Effect |
| Shear forces | Washout of well soluble EPS, accumulation of less soluble EPS, increase of stability of remaining matrix, sloughing off, erosion |
| Grazing by higher organisms (protozoa, larvae, snails etc.) | Selective removal of EPS and EPS producing organisms, formation of channels, destabilization of matrix |
Cell numbers in biofilms.
| System | Cell Density | Reference |
|---|---|---|
| 1010 mL−1 | [ | |
| Activated sludge | 1010–1011 mL−1 | [ |
| Anaerobic granules | ~1011 g−1 | Calculated from [ |
| Epilithic biofilms | 108–1010 mL−1 | [ |
| Marine snow | 109–1010 g−1 | [ |
Figure 5Control of biofilm formation by c-di-Guanidinemonophosphate (c-di-GMP). Concentration of c-di-GMP is regulated by DGC (Diguanylate cyclase; GGDEF domain: diguanylate cyclase), PDE 1 (Phosphodiesterase; EAL domain: diguanylate phosphodiesterase, linearizes c-di-GMP to 5′-pGpG), PDE (nonspecific cellular PDEs, further degrading 5′-pGpG to GMP), and PDE 2 (Phosphodiesterase; HD-GYP domain, metal dependent, unrelated to the EAL domain, linearizes c-di-GMP to 5′-pGpG, degrades 5′-pGpG further to GMP). pGpG—5′ phosphoguanylyl(3′,5′)guanosine; GMP—Guanosine-5-phosphate (from Krauss, G.-J., Nies, D. (Eds.): Ecological Biochemistry-Environmental and Interspecies Interactions today, VCH Weinheim, 2014, with permission).
Figure 6The dammned polymer matrix (J.C. Bryers, Univ. Washington, with permission).