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Effect of continuous aeration on bacterial oxidation of organic matter

Published online by Cambridge University Press:  15 May 2009

L. A. Allen
Affiliation:
Water Pollution Research Laboratory, Langley Road, Watford
G. E. Eden
Affiliation:
Water Pollution Research Laboratory, Langley Road, Watford
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Growth of bacteria in an infusion of flax under quiescent conditions resulted in the formation of an acidic liquor with an appreciable content of volatile acids. When a similar infusion was aerated by a continuous current of air, the liquid tended to become alkaline and the content of volatile acids was much smaller and in some cases negligible. Aeration reduced the polluting strength of the liquor, as measured by oxygen absorbed from permanganate and by the biochemical oxygen demand, by much larger amounts than did growth under quiescent conditions.

Experiments with infusion in which the natural flora was allowed to grow, and with sterile infusion inoculated with pure strains of different types of bacteria, showed that the general effect of aeration was to alter the metabolism of the bacteria in the direction of more complete oxidation of the substrate. Balance sheets for carbon showed that the organic carbon lost from the culture was accounted for by the CO2 evolved. Thus carbohydrates, which under anaerobic conditions were fermented to organic acids, neutral volatile compounds, and gases, were oxidized, when the conditions were sufficiently aerobic; to CO2 and water.

The magnitude of the effects observed depended largely on the nature of the organisms present, and partly on the strength of the infusion in which they grew. With pure cultures of Bact. coli, Bact. aerogenes and Bacillus subtilis, and with the natural mixed flora of the flax, aeration at moderate rates in bottles for 3–5 days reduced the value for oxygen absorbed from permanganate by 43–52 %, and the biochemical oxygen demand by 26–92 %, indifferent experiments. The organic carbon content of the infusion was reduced by 30–31 % by Bact. aerogenes, by Bacillus subtilis and by the mixed flora. With streptococci and with a strain of Achromobacterium the effects observed were very small. Aeration at higher rates with diffused air in small open tanks reduced the organic carbon content of a flax infusion by 50 % in about 80 hr., and of a beetroot infusion by 50 % in about 60 hr. Sugar was destroyed during the aeration and disappeared rapidly from the flax infusion in the early stages.

The work described in this paper was carried out in connexion with an investigation of retting of flax and disposal of waste waters, made, as an extramural research, for the Ministry of Supply as part of the programme of the Water Pollution Research Board of the Department of Scientific and Industrial Research. The paper is published by permission of the Chief Scientific Officer, Ministry of Supply, and of the Department.

Type
Research Article
Copyright
Copyright © Cambridge University Press 1946

References

REFERENCES

Allen, L. A. (1940). The influence of aeration on bacterial growth and on associated chemical changes. Proc. Soc. Agric. Bact. (Abstracts), p. 14.Google Scholar
Allen, L. A. (1944). Spore-forming bacteria causing soft rot of potatoes and the retting of flax. Nature, Lond., 153, 224.CrossRefGoogle Scholar
Beesley, R. M. (1914). Experiments on the rate of nitrification. J. Chem. Soc. 105, 1014.CrossRefGoogle Scholar
Carter, H. A. (1919). The microbiological retting of hemp, flax, and ramie. Text. Rec. 37, 127.Google Scholar
Cook, R. P. & Stephenson, M. (1928). Bacterial oxidations by molecular oxygen. I. The aerobic oxidation of glucose and its fermentation products in relation to the viability of the organism. Biochem. J. 22, 1368.CrossRefGoogle Scholar
Harden, A. (1901). The chemical action of B. coli communis and similar organisms on carbohydrates and allied compounds. J. Chem. Soc. 79, 610.CrossRefGoogle Scholar
Kluyver, A. J., Donker, H. J. L. & Hooft, F. V. t' (1925). Über die Bildung von Acetylmethylcarbinol und 2: 3-Butylenglykol im Stoffwechsel der Hefe. Biochem. Z. 161, 361.Google Scholar
Mills, E. V. (1931). The determination of organic carbon in sewage. J. Soc. Chem. Ind., Lond., 50, 375T.Google Scholar
Ministry of Health (1942). Methods of Chemical Analysis as applied to Sewage, and Sewage Effluents. London, H.M. Stationery Office.Google Scholar
Raistrick, H., and others (1931). Studies in the biochemistry of micro-organisms. Philos. Trans. B, 220.Google Scholar
Richards, E. H. & Cutler, D. W. (1933). Purification of waste waters from Beet Sugar Factories. Tech. Pap. Wat. Pollut. Res., Lond., no. 3.Google Scholar
Rossi, G. (1908). Industrial microbiological vegetal retting process by pectic aerobic microbes in a gas current. Brit. Pat. no. 6532.Google Scholar
Ruschmann, G. (1922). Vergleich von Röstverfahren in Fabrikbetrieb. I. Warm wasserbassin-, aërobe Röste und Peufaillitverfahren. Faserforschung, 2, 184.Google Scholar
Stephenson, M. & Whetham, M. D. (1924). The effect of oxygen supply on the metabolism of Bacillus coli communis. Biochem. J. 18, 498.CrossRefGoogle Scholar
Stiles, H. R., Peterson, W. H. & Fred, E. B. (1926). A rapid method for the determination of sugar in bacterial cultures. J. Bact. 12, 427.CrossRefGoogle ScholarPubMed
Thaysen, A. C. & Galloway, L. D. (1930). The Microbiology of Starch and Sugars. London: Oxford University Press.Google Scholar