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SELF-PROPELLED AERATORS Boris M. Khudenko, Associate Professor Department of Civil Engineering Wayne State University Detroit, Michigan 48202 For small communities and some industrial plants, extensive (low rate) treatment process, such as aerated lagoons, oxidation ditches and their modifications, offer several advantages over other types of treatment processes. These processes demonstrate better stability in treatment efficiency and simpler operation than activated sludge processes. Extensive treatment processes with forced aeration are also superior to nonaerated lagoons because mixing and aeration permit a two- to sixfold increase in pond or tank depth, and produce overall treatment rates at least two to four times greater than in nonaerated lagoons. The major disadvantage of extensive treatment methods with artificial aeration is their relatively high energy consumption, which is about 3-10 times greater per kg of BOD removed, than the conventional activated sludge process. Only a small fraction of this excessive energy consumption is due to the nitrification process. The high energy requirement is primarily due to the stationary nature of presently employed aeration equipment, including both anchored mechanical and diffused air aerators. Since the effectiveness of the aeration process depends on the amount of mixing in the reservoirs, thereby suspending the activated sludge, either four to ten times the number of stationary aeration units needed to satisfy the oxygen requirement are installed, or additional mixing devices are employed. Either of these approaches causes additional, and perhaps unnecessary, energy consumption. An alternative approach would be the use of mobile, and particularly self-propelled, aerators. Such devices can provide a more balanced energy usage between aeration and mixing, thus reducing energy consumption and operation costs for wastewater treatment in lagoons. The major parameters of self-propelled aerators are the linear velocity of their movement upon the water surface, their period of rotation, the service area, and oxygenation capacity. The determination of these parameters for mechanical and jet aerators is discussed in the following sections. SELF-PROPELLED MECHANICAL AERATORS A self-propelled mechanical aerator is illustrated in Figure 1. This aerator consists of an open-bladed-rotor and motor-gear mounted on a platform supported by floats. A hinged arm links the floating structure to the pile. The aerator is free to rotate around the pile. The hinges compensate for water level fluctuations in the basin. Linear Velocity and Period of Revolution The linear velocity and period of revolution of the aerator can be determined by equating the tractive, F, and drag, D, forces: I=D (1) The tractive force depends on the torque MQ and the arm length L, or, F = M„/L (2) 735
Object Description
Purdue Identification Number | ETRIWC198176 |
Title | Self-propelled aerators |
Author |
Khudenko, Boris M. |
Date of Original | 1981 |
Conference Title | Proceedings of the 36th Industrial Waste Conference |
Extent of Original | p. 735-746 |
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 | 2009-07-07 |
Capture Device | Fujitsu fi-5650C |
Capture Details | ScandAll 21 |
Resolution | 300 ppi |
Color Depth | 8 bit |
Description
Title | page 735 |
Collection Title | Engineering Technical Reports Collection, Purdue University |
Repository | Purdue University Libraries |
Rights Statement | Digital copyright Purdue University. All rights reserved. |
Language | eng |
Type (DCMI) | text |
Format | JP2 |
Capture Device | Fujitsu fi-5650C |
Capture Details | ScandAll 21 |
Transcript | SELF-PROPELLED AERATORS Boris M. Khudenko, Associate Professor Department of Civil Engineering Wayne State University Detroit, Michigan 48202 For small communities and some industrial plants, extensive (low rate) treatment process, such as aerated lagoons, oxidation ditches and their modifications, offer several advantages over other types of treatment processes. These processes demonstrate better stability in treatment efficiency and simpler operation than activated sludge processes. Extensive treatment processes with forced aeration are also superior to nonaerated lagoons because mixing and aeration permit a two- to sixfold increase in pond or tank depth, and produce overall treatment rates at least two to four times greater than in nonaerated lagoons. The major disadvantage of extensive treatment methods with artificial aeration is their relatively high energy consumption, which is about 3-10 times greater per kg of BOD removed, than the conventional activated sludge process. Only a small fraction of this excessive energy consumption is due to the nitrification process. The high energy requirement is primarily due to the stationary nature of presently employed aeration equipment, including both anchored mechanical and diffused air aerators. Since the effectiveness of the aeration process depends on the amount of mixing in the reservoirs, thereby suspending the activated sludge, either four to ten times the number of stationary aeration units needed to satisfy the oxygen requirement are installed, or additional mixing devices are employed. Either of these approaches causes additional, and perhaps unnecessary, energy consumption. An alternative approach would be the use of mobile, and particularly self-propelled, aerators. Such devices can provide a more balanced energy usage between aeration and mixing, thus reducing energy consumption and operation costs for wastewater treatment in lagoons. The major parameters of self-propelled aerators are the linear velocity of their movement upon the water surface, their period of rotation, the service area, and oxygenation capacity. The determination of these parameters for mechanical and jet aerators is discussed in the following sections. SELF-PROPELLED MECHANICAL AERATORS A self-propelled mechanical aerator is illustrated in Figure 1. This aerator consists of an open-bladed-rotor and motor-gear mounted on a platform supported by floats. A hinged arm links the floating structure to the pile. The aerator is free to rotate around the pile. The hinges compensate for water level fluctuations in the basin. Linear Velocity and Period of Revolution The linear velocity and period of revolution of the aerator can be determined by equating the tractive, F, and drag, D, forces: I=D (1) The tractive force depends on the torque MQ and the arm length L, or, F = M„/L (2) 735 |
Resolution | 300 ppi |
Color Depth | 8 bit |
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