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Biological Utilization of Cellulose L. B. POLKOWSKI, Professor of Sanitary Engineering Univeristy of Iowa Iowa City, Iowa R. C. LOEHR, Associate Professor University of Kansas, Lawrence, Kansas and G. A. ROHLICH, Director, Hydraulic & Sanitary Laboratory and T. IWATSU, Research Assistant University of Wisconsin Madison, Wisconsin INTRODUCTION This paper presents the summary of the results of two independent proj- ets: the utilization of cellulose by activated sludge and the anerobic digestion of domestic sludge with paper fiber sludge. The paper fiber sludge was obtained from the save-all units of a paper making industry. The utilization of cellulose by activated sludge has recently received attention by the Greater Chicago Municipal Sanitary District because ofthe occurrence of excess cellulose fiber in the dried sludge during certain seasons of the year. Hurwitz (1) reported that the cellulose concentration of the activated sludge in recent years was approximately 3.5 per cent on a dry weight basis during the winter months, whereas concentrations of cellulose during the summer months would be as low as 0.5 per cent. It was postulated that the activity of celluloytic bacteria was affected by the waste temperatures and that the rate of utilization of cellulose was reduced greatly during low temperature operation. Other factors were considered, such as suspended solids concentration of the mixed liquor, sludge age, and the variation of the cellulose concentration in the raw waste corresponding to seasonal changes. Recent studies by the Chicago Sanitary District havelseen made to evaluate the relative importance and relation of these variables to the utilization of cellulose in activated sludge treatment (1). The studies reported herein are on the effect of temperature on the rate of utilization of cellulose by activated sludge under laboratory conditions and on the effect of suspended solids concentration and initial concentration of cellulose in the mixed liquor on the rate of utilization. Cellulose is the primary constituent of sanitary papers, the use of which has increased significantly in the last 10 years in the U. S. The practice of garbage grinding also increases the cellulose content of sewage by the addition of the cellulosic material of plants. Cellulose, a polymer of glucose, has the assumed but generally accepted formulation shown in Figure 1 which shows the anhydroglucose residues constructed with the betaglucosidic bonds. The number ofanhydroglucose units - 566 -
Object Description
Purdue Identification Number | ETRIWC196247 |
Title | Biological utilization of cellulose |
Author |
Polkowski, Lawrence Benjamin, 1929- Loehr, Raymond C. Rohlich, G. A. (Gerard A.) Iwatsu, T. |
Date of Original | 1962 |
Conference Title | Proceedings of the seventeenth Industrial Waste Conference |
Conference Front Matter (copy and paste) | http://earchives.lib.purdue.edu/cdm4/document.php?CISOROOT=/engext&CISOPTR=9369&REC=18 |
Extent of Original | p. 566-582 |
Collection Title | Engineering Technical Reports Collection, Purdue University |
Repository | Purdue University Libraries |
Rights Statement | Digital object copyright Purdue University. All rights reserved. |
Language | eng |
Type (DCMI) | text |
Format | JP2 |
Date Digitized | 2009-05-18 |
Capture Device | Fujitsu fi-5650C |
Capture Details | ScandAll 21 |
Resolution | 300 ppi |
Color Depth | 8 bit |
Description
Title | page 566 |
Collection Title | Engineering Technical Reports Collection, Purdue University |
Repository | Purdue University Libraries |
Rights Statement | Digital object copyright Purdue University. All rights reserved. |
Language | eng |
Type (DCMI) | text |
Format | JP2 |
Capture Device | Fujitsu fi-5650C |
Capture Details | ScandAll 21 |
Transcript | Biological Utilization of Cellulose L. B. POLKOWSKI, Professor of Sanitary Engineering Univeristy of Iowa Iowa City, Iowa R. C. LOEHR, Associate Professor University of Kansas, Lawrence, Kansas and G. A. ROHLICH, Director, Hydraulic & Sanitary Laboratory and T. IWATSU, Research Assistant University of Wisconsin Madison, Wisconsin INTRODUCTION This paper presents the summary of the results of two independent proj- ets: the utilization of cellulose by activated sludge and the anerobic digestion of domestic sludge with paper fiber sludge. The paper fiber sludge was obtained from the save-all units of a paper making industry. The utilization of cellulose by activated sludge has recently received attention by the Greater Chicago Municipal Sanitary District because ofthe occurrence of excess cellulose fiber in the dried sludge during certain seasons of the year. Hurwitz (1) reported that the cellulose concentration of the activated sludge in recent years was approximately 3.5 per cent on a dry weight basis during the winter months, whereas concentrations of cellulose during the summer months would be as low as 0.5 per cent. It was postulated that the activity of celluloytic bacteria was affected by the waste temperatures and that the rate of utilization of cellulose was reduced greatly during low temperature operation. Other factors were considered, such as suspended solids concentration of the mixed liquor, sludge age, and the variation of the cellulose concentration in the raw waste corresponding to seasonal changes. Recent studies by the Chicago Sanitary District havelseen made to evaluate the relative importance and relation of these variables to the utilization of cellulose in activated sludge treatment (1). The studies reported herein are on the effect of temperature on the rate of utilization of cellulose by activated sludge under laboratory conditions and on the effect of suspended solids concentration and initial concentration of cellulose in the mixed liquor on the rate of utilization. Cellulose is the primary constituent of sanitary papers, the use of which has increased significantly in the last 10 years in the U. S. The practice of garbage grinding also increases the cellulose content of sewage by the addition of the cellulosic material of plants. Cellulose, a polymer of glucose, has the assumed but generally accepted formulation shown in Figure 1 which shows the anhydroglucose residues constructed with the betaglucosidic bonds. The number ofanhydroglucose units - 566 - |
Resolution | 300 ppi |
Color Depth | 8 bit |
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