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DETERMINATION OF ALKALINITY REQUIREMENTS FOR THE ANAEROBIC TREATMENT PROCESS Alan Li, Process Engineer Paul M. Sutton, Senior Process Engineer Dorr-Oliver, Incorporated Stamford, Connecticut 06904 INTRODUCTION It has long been recognized that control of pH is essential for the successful operation of the anaerobic process in wastewater treatment [1]. Methane producing bacteria are extremely sensitive to the changes in environmental conditions. Any effects on methane bacteria usually result in the accu- lation of volatile acids and a higher C02 content in the gas, both which tend to decrease the reactor pH. If the pH is not maintained due to a lack of buffering capacity, the condition will further retard the methanogenic activity and result in a process upset. Many municipal anaerobic digesters become "sour" as a result of inadequate pH control. Reactor pH is usually controlled near neutral by addition of alkalinity or alkalinity-producing chemicals to the reactors, although other methods such as reduction C02 in the gas phase, have been proposed [2]. For anaerobic treatment of industrial wastewaters containing little or no alkalinity, the costs associated with pH control can be very significant. For example approximately 10,900 kg (24,000 lbs) of sodium bicarbonate are required per day for anaerobically treating 3,780 m3/day (103 gal/day) of wastewater containing no alkalinity in order to maintain 2,000 mg/1 of alkalinity as CaC03. Although researchers have completed studies on pH control in anaerobic reactors, no single design approach has been accepted for estimating the alkalinity requirements. In the past, lime has been widely used for pH adjustment in the municipal anaerobic digester, and the dosage requirements for maintaining the pH between 6.5 and 7.0 were based on empirical experience. Addition of 4.5 to 6.8 kg (10 to 15 pounds) of lime per 1000 population per day, or per 28 m3 (1000 ft3) of digester capacity per day, was recommended for digester pH control [3,4], Further development in anaerobic process research considered the volatile acids in the digesters as the major demand for alkalinity, and volatile acid alkalinity was used to determine the alkalinity requirement for the digester without much success [5,6]. The concept of having enough bicarbonate alkalinity to maintain C02 equilibrium in the digester was proposed by Benta and Pomeroy [7] in the 1930's. Murray [8] used the concept to estimate the alkalinity requirement for the anaerobic treatment process with moderate success. This alkalinity and C02 equilibrium relation was discussed in great detail by Capri and Marais [9] and Loewenthal and Marais [10]. However, they all failed to include the alkalinity required for volatile acid neutralization. The purpose of this paper is to present a rational method for estimating the alkalinity requirements in the anaerobic treatment process. The method is based on the principle that the alkalinity required is mainly for the neutralization of carbonic and volatile acids. The results from a pilot plant study involving a two phase (acid stage followed by methane stage) anaerobic fluidized bed system (Anitron System™) were used to test the validity of the model. A process design procedure for pH control is proposed and illustrated in a design example. Finally, the paper also discusses the selection of pH chemicals for use in the anaerobic treatment process. 603
Object Description
Purdue Identification Number | ETRIWC198362 |
Title | Determination of alkalinity requirements for the anaerobic treatment process |
Author |
Li, Alan Y. Sutton, Paul M. |
Date of Original | 1983 |
Conference Title | Proceedings of the 38th Industrial Waste Conference |
Conference Front Matter (copy and paste) | http://e-archives.lib.purdue.edu/u?/engext,34749 |
Extent of Original | p. 603-614 |
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 | 2009-07-28 |
Capture Device | Fujitsu fi-5650C |
Capture Details | ScandAll 21 |
Resolution | 300 ppi |
Color Depth | 8 bit |
Description
Title | page 603 |
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 | DETERMINATION OF ALKALINITY REQUIREMENTS FOR THE ANAEROBIC TREATMENT PROCESS Alan Li, Process Engineer Paul M. Sutton, Senior Process Engineer Dorr-Oliver, Incorporated Stamford, Connecticut 06904 INTRODUCTION It has long been recognized that control of pH is essential for the successful operation of the anaerobic process in wastewater treatment [1]. Methane producing bacteria are extremely sensitive to the changes in environmental conditions. Any effects on methane bacteria usually result in the accu- lation of volatile acids and a higher C02 content in the gas, both which tend to decrease the reactor pH. If the pH is not maintained due to a lack of buffering capacity, the condition will further retard the methanogenic activity and result in a process upset. Many municipal anaerobic digesters become "sour" as a result of inadequate pH control. Reactor pH is usually controlled near neutral by addition of alkalinity or alkalinity-producing chemicals to the reactors, although other methods such as reduction C02 in the gas phase, have been proposed [2]. For anaerobic treatment of industrial wastewaters containing little or no alkalinity, the costs associated with pH control can be very significant. For example approximately 10,900 kg (24,000 lbs) of sodium bicarbonate are required per day for anaerobically treating 3,780 m3/day (103 gal/day) of wastewater containing no alkalinity in order to maintain 2,000 mg/1 of alkalinity as CaC03. Although researchers have completed studies on pH control in anaerobic reactors, no single design approach has been accepted for estimating the alkalinity requirements. In the past, lime has been widely used for pH adjustment in the municipal anaerobic digester, and the dosage requirements for maintaining the pH between 6.5 and 7.0 were based on empirical experience. Addition of 4.5 to 6.8 kg (10 to 15 pounds) of lime per 1000 population per day, or per 28 m3 (1000 ft3) of digester capacity per day, was recommended for digester pH control [3,4], Further development in anaerobic process research considered the volatile acids in the digesters as the major demand for alkalinity, and volatile acid alkalinity was used to determine the alkalinity requirement for the digester without much success [5,6]. The concept of having enough bicarbonate alkalinity to maintain C02 equilibrium in the digester was proposed by Benta and Pomeroy [7] in the 1930's. Murray [8] used the concept to estimate the alkalinity requirement for the anaerobic treatment process with moderate success. This alkalinity and C02 equilibrium relation was discussed in great detail by Capri and Marais [9] and Loewenthal and Marais [10]. However, they all failed to include the alkalinity required for volatile acid neutralization. The purpose of this paper is to present a rational method for estimating the alkalinity requirements in the anaerobic treatment process. The method is based on the principle that the alkalinity required is mainly for the neutralization of carbonic and volatile acids. The results from a pilot plant study involving a two phase (acid stage followed by methane stage) anaerobic fluidized bed system (Anitron System™) were used to test the validity of the model. A process design procedure for pH control is proposed and illustrated in a design example. Finally, the paper also discusses the selection of pH chemicals for use in the anaerobic treatment process. 603 |
Resolution | 300 ppi |
Color Depth | 8 bit |
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