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A Five Minute Solution for Stream Assimilative Capacity ARTHUR W. BUSCH, Professor Department of Environmental Engineering Rice University Houston, Texas INTRODUCTION One of the cornerstones of environmental management is the use of the maximum capacity of our natural waters to assimilate organic wastes. This capacity is called the stream assimilative or stream purification capacity. As was pointed out recently (1), discharging as much waste as possible to our natural waters is a policy of intentional pollution. Much work and many hundreds of thousands of dollars have gone into studies whose objective is to maximize intentional pollution. The intent of this paper is to show that if we insist on intentionally polluting our natural waters, the minimum capacity for assimilation, without lowering oxygen content below a pre-determined value, is the significant capacity and becomes the maximum available for intentional pollution. Discharge of any wastes in excess of this minimum capacity must involve a probabilistic analysis. The minimum assimilative capacity is set by the minimum reaeration capacity because reaeration is the only source of continuous oxygen supply. The minimum reaeration capacity thus is the maximum usable assimilative capacity for uniformly applied and distributed wastes. CONCEPTS Last year at this conference, a paper on aeration and oxygen transfer pointed out that in waste treatment aeration the effectiveness of esternal energy input is constrained by the biological reaction (2). In other words, we can not transfer oxygen faster than we use it. Natural reaeration of streams is exactly the opposite. In this case we can not count on using oxygen unless it is transferred into the water by natural phenomena or unless instream aeration is practiced. See Figure 1. This means that the assimulative or purification capacity of a body of water is set by the product of the minimum surface (mass) transfer coefficient, the maximum dissolved oxygen deficit and the surface area under consideration. The general expression for gas transfer to a liquid is dM = KLA(Cs-C) (1) dt Where Kj_ is the mass transfer coefficient, A is the interfacial surface area and Cs and C are saturation and ambient dissolved oxygen concentrations. For the worst condition in a natural body of water; i.e. no surface turbulence and highest temperature: 151
Object Description
Purdue Identification Number | ETRIWC197113 |
Title | Five minute solution for stream assimilative capacity |
Author | Busch, Arthur Winston, 1926- |
Date of Original | 1971 |
Conference Title | Proceedings of the 26th Industrial Waste Conference |
Conference Front Matter (copy and paste) | http://earchives.lib.purdue.edu/u?/engext,19214 |
Extent of Original | p. 151-155 |
Series | Engineering extension series no. 140 |
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 | 2009-06-25 |
Capture Device | Fujitsu fi-5650C |
Capture Details | ScandAll 21 |
Resolution | 300 ppi |
Color Depth | 8 bit |
Description
Title | page 151 |
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 | A Five Minute Solution for Stream Assimilative Capacity ARTHUR W. BUSCH, Professor Department of Environmental Engineering Rice University Houston, Texas INTRODUCTION One of the cornerstones of environmental management is the use of the maximum capacity of our natural waters to assimilate organic wastes. This capacity is called the stream assimilative or stream purification capacity. As was pointed out recently (1), discharging as much waste as possible to our natural waters is a policy of intentional pollution. Much work and many hundreds of thousands of dollars have gone into studies whose objective is to maximize intentional pollution. The intent of this paper is to show that if we insist on intentionally polluting our natural waters, the minimum capacity for assimilation, without lowering oxygen content below a pre-determined value, is the significant capacity and becomes the maximum available for intentional pollution. Discharge of any wastes in excess of this minimum capacity must involve a probabilistic analysis. The minimum assimilative capacity is set by the minimum reaeration capacity because reaeration is the only source of continuous oxygen supply. The minimum reaeration capacity thus is the maximum usable assimilative capacity for uniformly applied and distributed wastes. CONCEPTS Last year at this conference, a paper on aeration and oxygen transfer pointed out that in waste treatment aeration the effectiveness of esternal energy input is constrained by the biological reaction (2). In other words, we can not transfer oxygen faster than we use it. Natural reaeration of streams is exactly the opposite. In this case we can not count on using oxygen unless it is transferred into the water by natural phenomena or unless instream aeration is practiced. See Figure 1. This means that the assimulative or purification capacity of a body of water is set by the product of the minimum surface (mass) transfer coefficient, the maximum dissolved oxygen deficit and the surface area under consideration. The general expression for gas transfer to a liquid is dM = KLA(Cs-C) (1) dt Where Kj_ is the mass transfer coefficient, A is the interfacial surface area and Cs and C are saturation and ambient dissolved oxygen concentrations. For the worst condition in a natural body of water; i.e. no surface turbulence and highest temperature: 151 |
Resolution | 300 ppi |
Color Depth | 8 bit |
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