Correlation of Coliform Growth Response With Other Water Quality Parameters

bacteria has also been shown to interfere with the detection of coliform bacteria. Further, and perhaps most important, members of the total coliform group of bacteria themselves have been implicated in regrowth problems, thus $ving rise to major compliance violations. Bacterial regrowth is affected by a variety of factors. The temperature of the water has been shown to play a major role in bacterial regrowth. An increase in heterotrophic plate count (HPC) organisms has been associated with increasing temperatures following a late spring-summer-autumn sequence in utilities experiencing coliform problems.3 The type of water treatment that is employed by a utility may have a direct impact on microbial growth. It has been demonstrated that the use of ozone in the treatment of water with high humic content, without the subsequent removal of the oxidation products, increases microbial growth in the distribution system.4 This finding is of particular interest because of the proposed increased use of ozonation by water utilities. The incorporation of biological unit processes in water treatment can also affect the nutrient status of the product water. Biological treatment of drinking water, although rarely used in the United States, is common in Europe where the biooxidation of organic matter and ammonia has been demonstrated to be beneficial and cost-efficient. The velocity of water flowing through the mains is an important factor influencing microbial colonization and growth in the distribution system. Pipe sectionswith high water velocities tend to limit microbial protection and reduce sediment accumulation, thus minimizing nutrient entrap ment and protection from exposure to the disinfectant. Conversely, areas of slow flow and dead-end locations have been statistically correlated with water quality deterioration? The presence of iron tubercles has also been associated with microbial growth, especially with colonization by coliform bacteria.6 The maintenance of an adequate disinfectant residual is universally recom

[1]  LeVerne D. Hudson,et al.  Coliforms in a water distribution system: a remedial approach , 1983 .

[2]  S. Edberg,et al.  Phenotypic characteristics of coliform and noncoliform bacteria from a public water supply compared with regional and national clinical species , 1986, Applied and environmental microbiology.

[3]  P. Servais,et al.  Determination of the biodegradable fraction of dissolved organic matter in waters , 1987 .

[4]  Shankha K. Banerji,et al.  Biologically mediated corrosion and its effects on water quality in distribution systems , 1980 .

[5]  Dirk van der Kooij,et al.  Determining the concentration of easily assimilable organic carbon in drinking water , 1982 .

[6]  M. Lechevallier,et al.  Examination and characterization of distribution system biofilms , 1987, Applied and environmental microbiology.

[7]  J. Fry,et al.  Development and Operational Implementation of a Modified and Simplified Method for Determination of Assimilable Organic Carbon (AOC) in Drinking Water , 1989 .

[8]  J S Colbourne,et al.  Techniques for the assessment of growth of micro-organisms on plumbing materials used in contact with potable water supplies. , 1977, The Journal of applied bacteriology.

[9]  John T. Wierenga,et al.  Recovery of coliforms in the presence of a free chlorine residual , 1985 .

[10]  Vernon L. Snoeyink,et al.  Achieving Biologically Stable Drinking Water , 1984 .

[11]  Richard S Tobin,et al.  Factors affecting coliform bacteria growth in distribution systems , 1982 .

[12]  W. Hijnen,et al.  Substrate Utilization by an Oxalate-Consuming Spirillum Species in Relation to Its Growth in Ozonated Water , 1984, Applied and environmental microbiology.

[13]  E. Rice,et al.  Bioassay procedure for predicting coliform bacterial growth in drinking water , 1990 .

[14]  Edwin E. Geldreich,et al.  Occurrence, Significance, and Detection of Klebsiella in Water Systems , 1987 .