Dispersal dynamics of groundwater bacteria

Dispersal of bacteria in saturated, porous soils can be characterized by the partitioning of cells between the aqueous and solid phases, as a result of the physical and chemical nature of the soil and water and cell surface modifications. The purpose of this work is to understand variations in partitioning as a consequence of the nutrient conditions and to use this information in mathematical models to predict the dispersal rate of bacteria in aquifer material. Two different models were used to describe dispersal: an advective-dispersive-sorptive model with a first order kinetic sink term to account for irreversible cell reactions, such as death and sorption; and a two-site reaction model, in which the retardation was assumed to be determined by two types of sites, one characterized by instantaneous equilibrium sorption reactions and the other by kinetic nonequilibrium reactions. Water-saturated sand columns were used as continuous-flow groundwater microcosms to test the models under different nutrient regimes. Two strains of indigenous groundwater bacteria were isolated from aquifer material and labelled with3H-alanine,14C-pyruvic acid,3H-glucose, and3H-adenosine for different measurements of sorption and dispersal, which were estimated from breakthrough curves. Both experimental data and model variables showed that dispersal of bacteria was a dynamic nonequilibrium process, possibly shaped by two subpopulations, one strongly, even irreversibly, adsorbing to the solid particles, and one with very slow adsorption kinetics. The cell surfaces were modified in response to the growth conditions, which was demonstrated by hydrophobic and electrostatic interaction chromatography. Cell surface hydrophobicity was about eight times higher in groundwater than in eutrophic lake water. The partition coefficient varied between 12.6 in the groundwater and 6.4 in the lake water, indicating the prime importance of hydrophobic binding for attachment in low nutrient conditions. The partitioning was also sensitive to the hydrodynamics of the system and the oxygen supply, as demonstrated by comparison of sorption in agitated test tubes, gently shaken vials, and air-flushed bottles. Sorption kinetics were demonstrated in a continuous flow cell. About 45% of a population was associated with sand particles with a continuous flow of pure groundwater and as little as 20% in lake water. However, more than 50% of the bacteria in the aqueous phase were associated with suspended material of less than 60 μm in diameter. This association may enhance dispersal for example, by size exclusion of the colloidal material in the interstitial pores.

[1]  G. H. Simonson,et al.  Survival and Movement of Fecal Indicator Bacteria in Soil under Conditions of Saturated Flow 1 , 1978 .

[2]  L. Weiss,et al.  Short-term interactions between cell surfaces , 1972 .

[3]  M. Sleigh,et al.  The forces on microorganisms at surfaces in flowing water , 1985 .

[4]  G. W. Thomas,et al.  Transport of Escherichia coli through intact and disturbed soil columns , 1985 .

[5]  R. Greensmith,et al.  Statistical Methods in Research and Production , 1973 .

[6]  D. R. Nielsen,et al.  Water flow and solute transport processes in the unsaturated zone , 1986 .

[7]  H. Busscher,et al.  Physico-chemical surface characteristics and adhesive properties of Streptococcus salivarius strains with defined cell surface structures , 1987 .

[8]  K. Marshall,et al.  Adhesion and growth of bacteria at surfaces in oligotrophic habitats , 1988 .

[9]  A. Klute,et al.  Convective‐dispersive solute transport with a combined equilibrium and kinetic adsorption model , 1977 .

[10]  R. Y. Morita Starvation-Survival of Heterotrophs in the Marine Environment , 1982 .

[11]  J. Marxsen Investigations into the number of respiring bacteria in groundwater from sandy and gravelly deposits , 1988, Microbial Ecology.

[12]  Jack C. Parker,et al.  Determining transport parameters from laboratory and field tracer experiments , 1984 .

[13]  J. W. Biggar,et al.  Nitrogen Transformations in Soil During Leaching: II. Steady State Nitrification and Nitrate Reduction 1 , 1974 .

[14]  Marylynn V. Yates,et al.  Modeling microbial fate in the subsurface environment , 1988 .

[15]  M. Fletcher,et al.  Are Solid Surfaces of Ecological Significance to Aquatic Bacteria , 1982 .

[16]  J. W. Biggar,et al.  Nitrogen Transformations in Soil During Leaching; I. Theoretical Considerations1 , 1974 .

[17]  M. Chaudhury,et al.  The role of van der Waals forces and hydrogen bonds in “hydrophobic interactions” between biopolymers and low energy surfaces , 1986 .

[18]  J. Laseter,et al.  Adsorption and concentration of dissolved carbon-14 DDT by coloring colloids in surface waters , 1972 .

[19]  W. J. Alves,et al.  Analytical solutions of the one-dimensional convective-dispersive solute transport equation , 1982 .

[20]  P. Pollard,et al.  Validity of the tritiated thymidine method for estimating bacterial growth rates: measurement of isotope dilution during DNA synthesis , 1984, Applied and environmental microbiology.

[21]  J. Lawrence,et al.  Detachment ofPseudomonas fluorescens from biofilms on glass surfaces in response to nutrient stress , 1989, Microbial Ecology.

[22]  G. J. Farquhar,et al.  Modeling of leachate organic migration and attenuation in groundwaters below sanitary landfills , 1982 .

[23]  M. V. van Loosdrecht,et al.  Electrophoretic mobility and hydrophobicity as a measured to predict the initial steps of bacterial adhesion , 1987, Applied and environmental microbiology.

[24]  John C. Romero,et al.  The Movement of Bacteria and Viruses Through Porous Media , 1970 .

[25]  Ronald D. Jones,et al.  A Study on the lack of [methyl-3H] thymidine uptake and incorporation by chemolithotrophic bacteria , 1989, Microbial Ecology.

[26]  R. Lindqvist,et al.  Influence of macromolecules on chemical transport , 1989 .

[27]  Asaf Pekdeger,et al.  Persistence and transport of bacteria and viruses in groundwater — a conceptual evaluation , 1988 .

[28]  William A. Jury,et al.  A Transfer Function Model of Solute Transport Through Soil: 2. Illustrative Applications , 1986 .

[29]  P. Sharma,et al.  Mechanisms of microbial movement in subsurface materials , 1989, Applied and environmental microbiology.

[30]  R. Ward,et al.  Development of a bacterial transport model for coarse soils , 1989 .

[31]  G. Bitton,et al.  Movement and retention of Klebsiella aerogenes in soil columns , 1974, Plant and Soil.

[32]  A. Nehrkorn,et al.  Microbial communities in the saturated groundwater environment I: Methods of isolation and characterization of heterotrophic bacteria , 1988, Microbial Ecology.

[33]  Albert J. Valocchi,et al.  Validity of the local equilibrium assumption for modeling sorbing solute transport through homogeneous soils , 1985 .

[34]  C. Enfield,et al.  Macromolecular Transport of Hydrophobic Contaminants in Aqueous Environments. , 1988 .

[35]  Richard L. Smith,et al.  Transport of microspheres and indigenous bacteria through a sandy aquifer: Results of natural- and forced-gradient tracer experiments , 1989 .

[36]  S. Kjelleberg,et al.  Starvation-Induced Effects on Bacterial Surface Characteristics , 1984, Applied and environmental microbiology.

[37]  K. H. Coats,et al.  Dead-End Pore Volume and Dispersion in Porous Media , 1964 .

[38]  G. Bengtsson,et al.  Ultrafiltration cell for sorption and biodegradation experiments , 1986 .

[39]  T. Stenström,et al.  Bacterial hydrophobicity, an overall parameter for the measurement of adhesion potential to soil particles , 1989, Applied and environmental microbiology.

[40]  C. Travis,et al.  Survey of sorption relationships for reactive solutes in soil , 1981 .

[41]  A. Pekdeger,et al.  Concepts of a survival and transport model of pathogenic bacteria and viruses in groundwater , 1981 .

[42]  G. Kling,et al.  Transport of Antibiotic-resistant Escherichia coli Through Western Oregon Hillslope Soils Under Conditions of Saturated Flow 1 , 1978 .

[43]  J. Lawrence,et al.  Behavior ofPseudomonas fluorescens within the hydrodynamic boundary layers of surface microenvironments , 1987, Microbial Ecology.

[44]  D. Balkwill,et al.  Characterization of Subsurface Bacteria Associated with Two Shallow Aquifers in Oklahoma , 1985, Applied and environmental microbiology.

[45]  Durell C. Dobbins,et al.  Microbial Biomass, Activity, and Community Structure in Subsurface Soils , 1986 .

[46]  L. Aylmore,et al.  COMPETITIVE ADSORPTION DURING SOLUTE TRANSPORT IN SOILS: 1. MATHEMATICAL MODELS , 1983 .

[47]  Göran Bengtsson,et al.  Growth and metabolic flexibility in groundwater bacteria , 1989, Microbial Ecology.

[48]  M. V. van Loosdrecht,et al.  The role of bacterial cell wall hydrophobicity in adhesion , 1987, Applied and environmental microbiology.

[49]  Warren W. Wood,et al.  Use of Baker's Yeast to Trace Microbial Movement in Ground Water , 1978 .

[50]  G. Southworth,et al.  Comparison of models that describe the transport of organic compounds in macroporous soil , 1987 .

[51]  Sharron McEldowney,et al.  Effect of Growth Conditions and Surface Characteristics of Aquatic Bacteria on Their Attachment to Solid Surfaces , 1986 .

[52]  H. Busscher,et al.  Specific and non-specific interactions in bacterial adhesion to solid substrata , 1987 .

[53]  M. Simon Biomass and production of small and large free‐living and attached bacteria in Lake Constance1 , 1987 .

[54]  M. Yavuz Corapcioglu,et al.  Transport and fate of microorganisms in porous media: A theoretical investigation , 1984 .

[55]  T. M. Ballard Role of Humic Carrier Substances in DDT Movement through Forest Soil1 , 1971 .

[56]  Physiological characterization of heterotrophic bacterial communities from selected aquatic environments , 1985, Microbial Ecology.

[57]  R. G. Gilbert,et al.  Virus and bacteria removal from wastewater by land treatment , 1976, Applied and environmental microbiology.

[58]  C. M. Brown,et al.  Surface-associated growth. , 1982, Philosophical transactions of the Royal Society of London. Series B, Biological sciences.

[59]  P. Burcar,et al.  Interaction of pesticides with natural organic material , 1969 .