Analysis of Microbiological Characteristics of Wastewater Along the Polishing Sequence of a Treatment Plant

Microbial populations were studied by plate counts and flow cytometry along the polishing sequence of a wastewater plant. The comparison between plate count and flow cytometry showed comparable trends, but plate counts detected less than 10% of the total intact bacteria counted by flow cytometry. Six months monitoring showed that, in spite of the high ozone doses, the disinfection effect of ozonation was insignificant. This is in agreement with the variability of ozone demand, not only related to chemical oxygen demand or total suspended solids. Membrane-intact bacterial population decreased after ozonation, slightly regrew between ozone and biological activated carbon (BAC), and sharply increased after BAC, probably for damaged bacteria regrowth and saprophytes release; BAC effluent had the highest bacterial counts. Preliminary investigations on the effluent microbial composition showed that the beta Proteobacteria subclass is the most represented in the BAC effluent, whereas the alpha subclass is the most sensitive to ozone effect.

[1]  James M. Montgomery,et al.  Water Treatment Principles and Design , 1985 .

[2]  J. Perkowski,et al.  Application of Ozone in Textile Wastewater Treatment , 1996 .

[3]  A. M. Mckay,et al.  Viable but non‐culturable forms of potentially pathogenic bacteria in water , 1992 .

[4]  R. Amann,et al.  Flow cytometric analysis of activated sludge with rRNA-targeted probes , 1995, Applied and environmental microbiology.

[5]  R Amann,et al.  Phylogenetic analysis and in situ identification of bacteria in activated sludge , 1997, Applied and environmental microbiology.

[6]  F. Rakoczi Multistage ozone treatment of dye waste , 1991 .

[7]  R. Amann,et al.  Optimizing fluorescent in situ hybridization with rRNA-targeted oligonucleotide probes for flow cytometric identification of microorganisms. , 1993, Cytometry.

[8]  P. McKay,et al.  Flow cytometric analysis. , 2000, Methods in molecular medicine.

[9]  K. Schleifer,et al.  Phylogenetic Oligodeoxynucleotide Probes for the Major Subclasses of Proteobacteria: Problems and Solutions , 1992 .

[10]  R. L. Wolfe,et al.  Assessment of the bacteriological activity associated with granular activated carbon treatment of drinking water , 1990, Applied and environmental microbiology.

[11]  Alessandra Ghiani,et al.  Resolution of Viable and Membrane-Compromised Bacteria in Freshwater and Marine Waters Based on Analytical Flow Cytometry and Nucleic Acid Double Staining , 2001, Applied and Environmental Microbiology.

[12]  D A Stahl,et al.  Fluorescent-oligonucleotide probing of whole cells for determinative, phylogenetic, and environmental studies in microbiology , 1990, Journal of bacteriology.

[13]  K. Schleifer,et al.  Probing activated sludge with oligonucleotides specific for proteobacteria: inadequacy of culture-dependent methods for describing microbial community structure , 1993, Applied and environmental microbiology.

[14]  M. Notarnicola,et al.  Advanced treatment and disinfection for municipal wastewater reuse in agriculture , 1999 .

[15]  M. Labra,et al.  Two and three-color fluorescence flow cytometric analysis of immunoidentified viable bacteria. , 2000, Cytometry.

[16]  R. Schneider,et al.  The effect of growth conditions on survival and recovery of Klebsiella oxytoca after exposure to chlorine , 1997 .

[17]  J. P. Gould,et al.  The Kinetics of Ozonolysis of Synthetic Dyes , 1987 .

[18]  J. Oliver,et al.  In vivo resuscitation, and virulence towards mice, of viable but nonculturable cells of Vibrio vulnificus , 1995, Applied and environmental microbiology.

[19]  M Salgot,et al.  Biological control tools for wastewater reclamation and reuse. A critical review. , 2001, Water science and technology : a journal of the International Association on Water Pollution Research.