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Trickling Filter Theories A. W. BUSCH, Professor Rice University Houston, Texas G. A. HUGHMARK, Senior Chemical Engineering Associate Ethyl Corporation Baton Rouge, Louisiana INTRODUCTION Several models have been proposed to represent the trickling filter used for the biological treatment of organic-bearing waste. These models represent two general categories. The first is a "curve-fitting" type of model that fits the typical overall response of a filter to variables such as BOD loading and filter depth. The Velz (1) model is an example: L ■D 10"KD (1) L =s removable BOD Lp = remaining removable BOD at filter depth D K = logarithmic constant of BOD removal for filter Stack (2) revised this model and proposed that the fraction of BOD that is consumed in one pass throughone unit depth be used in place of the Velz logarithmic constant. Empirical models of this type are useful in the interpolation of experimental data but must be used with caution for extrapolation. The second is mechanistic models in which mass transfer and reaction kinetics are considered as distinct processes. Atkinson, Busch, and Dawkins (3) proposed a model for film flow on a vertical wall in which the reaction rate controlled and the concentration gradients of the substrate and oxygen were negligible. Swilley, Atkinson, Busch, and Williams (4) extended the model to consider dillusional resistance for continuous liquid application and laminar flow of the film on an inclined surface. Experimental data obtained on an inclined plate showed that the magnitude of the reaction rate for a glucose solution is such that the liquid phase resistance is significant and can be controlling. The complexity of the model is greatly increased when mass transfer is included and becomes impractical for analytic solution of anything other than a laminar film. The purpose of this paper is to present a model that is applicable to solution by a digital computer and can be used to represent eddy mixing in the liquid film. CELL MODEL The mathematical model selected is the "cell" model. This assumes that the substrate and oxygen are consumed at the surface of the inclined plate and - 766 -
Object Description
Purdue Identification Number | ETRIWC196862 |
Title | Trickling filter theories |
Author |
Busch, Arthur Winston, 1926- Hughmark, G. A. |
Date of Original | 1968 |
Conference Title | Proceedings of the 23rd Industrial Waste Conference |
Conference Front Matter (copy and paste) | http://earchives.lib.purdue.edu/u?/engext,15314 |
Extent of Original | p. 766-771 |
Series |
Engineering extension series no. 132 Engineering bulletin v. 53, no. 2 |
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 | 2009-05-20 |
Capture Device | Fujitsu fi-5650C |
Capture Details | ScandAll 21 |
Resolution | 300 ppi |
Color Depth | 8 bit |
Description
Title | page 766 |
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 | Trickling Filter Theories A. W. BUSCH, Professor Rice University Houston, Texas G. A. HUGHMARK, Senior Chemical Engineering Associate Ethyl Corporation Baton Rouge, Louisiana INTRODUCTION Several models have been proposed to represent the trickling filter used for the biological treatment of organic-bearing waste. These models represent two general categories. The first is a "curve-fitting" type of model that fits the typical overall response of a filter to variables such as BOD loading and filter depth. The Velz (1) model is an example: L ■D 10"KD (1) L =s removable BOD Lp = remaining removable BOD at filter depth D K = logarithmic constant of BOD removal for filter Stack (2) revised this model and proposed that the fraction of BOD that is consumed in one pass throughone unit depth be used in place of the Velz logarithmic constant. Empirical models of this type are useful in the interpolation of experimental data but must be used with caution for extrapolation. The second is mechanistic models in which mass transfer and reaction kinetics are considered as distinct processes. Atkinson, Busch, and Dawkins (3) proposed a model for film flow on a vertical wall in which the reaction rate controlled and the concentration gradients of the substrate and oxygen were negligible. Swilley, Atkinson, Busch, and Williams (4) extended the model to consider dillusional resistance for continuous liquid application and laminar flow of the film on an inclined surface. Experimental data obtained on an inclined plate showed that the magnitude of the reaction rate for a glucose solution is such that the liquid phase resistance is significant and can be controlling. The complexity of the model is greatly increased when mass transfer is included and becomes impractical for analytic solution of anything other than a laminar film. The purpose of this paper is to present a model that is applicable to solution by a digital computer and can be used to represent eddy mixing in the liquid film. CELL MODEL The mathematical model selected is the "cell" model. This assumes that the substrate and oxygen are consumed at the surface of the inclined plate and - 766 - |
Resolution | 300 ppi |
Color Depth | 8 bit |
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