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Thickening of Compressible Sludges JON A. COLE, Associate Professor Wala Wala College College Place, Washington 99324 LAWRENCE B. POLKOWSKI, Professor JOHN A. HOOPES, Associate Professor Civil and Environmental Engineering University of Wisconsin Madison, Wisconsin 53706 INTRODUCTION To determine the cost of wastewater treatment which is attributable to solids handling would require a definitive description of waste characteristics and the treatment process employed. General capital and operation costs place the proportion of waste treatment funds expended in the handling of solids in the range of one-third to one-half of total costs (1.2. 3.4, 5). Units used in production and processing of solids are many, including a variety of modifications of basic forms. Solids concentration increase is a major objective in some operations, such as flotation, gravity thickening, centrifugation, and drying beds. While legal requirements dictate that the primary objective of final settling tanks is clarification, considerable design effort and operational attention is given toward concentration of the settled material, expecially when return sludge consistency affects other unit operations. Disposal efficiency for excess solids is also dependent upon underflow concentration, often leading to use of a separate thickening unit. Sludge concentration is likewise a necessary aspect of second stage and single stage digestion. Concentration of solids involves drawing particles together in closer proximity as well as release of water from the suspension. Gravity thickening, which contains both of these aspects as well as being related to the aforementioned unit operations, was chosen as a most likely component for the study of compressible sludges. In as much as design techniques employed for gravity thickeners are largely a result of theory developed for incompressible slurries, it is not surprising that these units are commonly over designed (6, 7, 8) or at the least poorly understood with respect to wastewater applications. THICKENER DESIGN FOR NONCOMPRESSIBLE SLUDGES Rational procedures for the design of continuous sludge thickening facilities were not developed with highly theoretical considerations but rather employed the batch laboratory procedure of observing the time dependent subsidence of the interface which forms between a concentrating material and the liquid being released. This procedure, which is still widely preferred more than fifty years after its inception, was used by Coe and Clevenger (9) to calculate the required cross-sectional area for a continuous thickener. Although their design formula was used for investigation of concentrations ranging from the feed to the underflow, the authors understood that other factors affected the settling rate giving different shapes to batch interface subsidence curves under different conditions. It was suggested that the conditions found in practice should be duplicated or that multiple tests be conducted over the range of conditions expected. Kynch (10) made a major contribution to thickening theory using continuity relationships to describe batch interface subsidence velocities. Assuming that the settling velocity v, is a function only of local particle concentration, c, he showed that the layers of uniform concentration, which are propagated upward through the slurry, travel at constant velocities, U, (traces in Figure I a). 293
Object Description
Purdue Identification Number | ETRIWC197328 |
Title | Thickening of compressible sludges |
Author |
Cole, Jon A. Polkowski, Lawrence Benjamin, 1929- Hoopes, John A. |
Date of Original | 1973 |
Conference Title | Proceedings of the 28th Industrial Waste Conference |
Conference Front Matter (copy and paste) | http://earchives.lib.purdue.edu/u?/engext,23197 |
Extent of Original | p. 293-308 |
Series | Engineering extension series no. 142 |
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 | 2009-06-02 |
Capture Device | Fujitsu fi-5650C |
Capture Details | ScandAll 21 |
Resolution | 300 ppi |
Color Depth | 8 bit |
Description
Title | page 293 |
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 | Thickening of Compressible Sludges JON A. COLE, Associate Professor Wala Wala College College Place, Washington 99324 LAWRENCE B. POLKOWSKI, Professor JOHN A. HOOPES, Associate Professor Civil and Environmental Engineering University of Wisconsin Madison, Wisconsin 53706 INTRODUCTION To determine the cost of wastewater treatment which is attributable to solids handling would require a definitive description of waste characteristics and the treatment process employed. General capital and operation costs place the proportion of waste treatment funds expended in the handling of solids in the range of one-third to one-half of total costs (1.2. 3.4, 5). Units used in production and processing of solids are many, including a variety of modifications of basic forms. Solids concentration increase is a major objective in some operations, such as flotation, gravity thickening, centrifugation, and drying beds. While legal requirements dictate that the primary objective of final settling tanks is clarification, considerable design effort and operational attention is given toward concentration of the settled material, expecially when return sludge consistency affects other unit operations. Disposal efficiency for excess solids is also dependent upon underflow concentration, often leading to use of a separate thickening unit. Sludge concentration is likewise a necessary aspect of second stage and single stage digestion. Concentration of solids involves drawing particles together in closer proximity as well as release of water from the suspension. Gravity thickening, which contains both of these aspects as well as being related to the aforementioned unit operations, was chosen as a most likely component for the study of compressible sludges. In as much as design techniques employed for gravity thickeners are largely a result of theory developed for incompressible slurries, it is not surprising that these units are commonly over designed (6, 7, 8) or at the least poorly understood with respect to wastewater applications. THICKENER DESIGN FOR NONCOMPRESSIBLE SLUDGES Rational procedures for the design of continuous sludge thickening facilities were not developed with highly theoretical considerations but rather employed the batch laboratory procedure of observing the time dependent subsidence of the interface which forms between a concentrating material and the liquid being released. This procedure, which is still widely preferred more than fifty years after its inception, was used by Coe and Clevenger (9) to calculate the required cross-sectional area for a continuous thickener. Although their design formula was used for investigation of concentrations ranging from the feed to the underflow, the authors understood that other factors affected the settling rate giving different shapes to batch interface subsidence curves under different conditions. It was suggested that the conditions found in practice should be duplicated or that multiple tests be conducted over the range of conditions expected. Kynch (10) made a major contribution to thickening theory using continuity relationships to describe batch interface subsidence velocities. Assuming that the settling velocity v, is a function only of local particle concentration, c, he showed that the layers of uniform concentration, which are propagated upward through the slurry, travel at constant velocities, U, (traces in Figure I a). 293 |
Resolution | 300 ppi |
Color Depth | 8 bit |
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