Towards a reduction in excess sludge production in activated sludge processes: biomass physicochemical treatment and biodegradation

Abstract To decrease activated sludge production, microbial cell lysis can be amplified to enhance cryptic growth (biomass growth on lysates). Cell breakage techniques (thermal, alkaline, acid) were studied to generate Alcaligenes eutrophus and sludge lysates and to evaluate their biodegradability. Gentle treatment conditions produced the best results. Complete cell deactivation was obtained for temperatures higher than 55 °C. The release kinetics were similar for temperatures varying from 60 °C to 100 °C. A 20-min incubation was suitable for reaching 80% of the maximum releasable carbon. In thermal-chemical hydrolysis, NaOH was the most efficient for inducing cell lysis. Carbon release was a two-step process. First an immediate release occurred, which was of the same order of magnitude for A. eutrophus and sludge [100–200 mg dissolved organic C (DOC) g total suspended solids (TSS)−1], followed by a post-treatment release. The second step was virtually equivalent to the first for sludge, and weaker for A. eutrophus (<50 mg DOC g TSS−1). The biodegradability of the soluble fraction, both the immediate and the post-treatment carbon release, was investigated. The optimal degradation yield, obtained with sludge cells, reached 55% after 48 h of incubation and 80% after 350 h. The most consistent lysis and biodegradation results occurred at pH 10 and 60 °C after a 20-min incubation.

[1]  G. Hamer,et al.  Death and lysis during aerobic thermophilic sludge treatment: Characterization of recalcitrant products , 1994 .

[2]  Jörg Schwedes,et al.  Anaerobic digestion and dewatering characteristics of mechanically disintegrated excess sludge , 1997 .

[3]  James D. Bryers,et al.  The death and lysis of microorganisms in environmental processes , 1986 .

[4]  Steven E. Woodard,et al.  A hydrolysis/thickening/filtration process for the treatment of waste activated sludge , 1994 .

[5]  Kinetic behavior of heterogeneous populations in completely mixed reactors , 1967 .

[6]  Sebastiaan A.L.M. Kooijman,et al.  Effects of protozoa on carbon mineralization in activated sludge , 1996 .

[7]  J. Block,et al.  Composition and activity of activated sludge under starvation conditions , 1993 .

[8]  R. Stanier,et al.  Dissimilation of Aromatic Compounds by Alcaligenes eutrophus , 1971, Journal of bacteriology.

[9]  Colin Anthony Mason Microbial death, lysis and "cryptic"growth , 1986 .

[10]  A. Tiehm,et al.  The use of ultrasound to accelerate the anaerobic digestion of sewage sludge , 1997 .

[11]  A. Middelberg,et al.  Process-scale disruption of microorganisms. , 1995, Biotechnology advances.

[12]  G. Hamer,et al.  ACTIVITY, DEATH AND LYSIS DURING MICROBIAL GROWTH IN A CHEMOSTAT , 1986 .

[13]  Thomas Welander,et al.  Reducing sludge production in aerobic wastewater treatment through manipulation of the ecosystem , 1996 .

[14]  H. Ødegaard,et al.  Thermal hydrolysate as a carbon source for denitrification , 1996 .

[15]  G. Goma,et al.  Decreased sludge production strategy for domestic wastewater treatment , 1994 .

[16]  G. Goma,et al.  Membrane bioreactors for the evaluation of maintenance phenomena in wastewater treatment , 1990 .

[17]  T. Egli,et al.  Theoretical Analysis of Media Used in the Growth of Yeasts on Methanol , 1981 .

[18]  Jih‐Gaw Lin,et al.  Alkaline and ultrasonic pretreatment of sludge before anaerobic digestion , 1997 .

[19]  H. Yasui,et al.  An innovative approach to reduce excess sludge production in the activated sludge process , 1994 .

[20]  N. Aoki,et al.  Development of High-Performance Thermophilic Two-Phase Digestion Process , 1991 .

[21]  J. Chudoba Quantitative estimation in cod units of refractory organic compounds produced by activated sludge microorganisms , 1985 .