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18 ANAEROBIC TREATMENT OF HIGH STRENGTH, HIGH SULFATE WASTES Barry L. Hilton, Research Assistant Jan A. Oleszkiewicz, Associate Professor Department of Civil Engineering The University of Manitoba Winnipeg, Manitoba Canada R3T 2N2 INTRODUCTION The high rate of accumulation of sulfates constitutes a growing environmental concern. Large quantities of sulfates are generated by the electric power industry from flue gas desulfurization sludges. The pulp and paper industry, pharmaceutical industry, and segments of the food industry produce effluents which are high in sulfates and other species of oxidized sulfur compounds. The application of methanogenic treatment processes to these wastes may be hindered by the resulting reduction of these oxidized sulfur species by sulfate reducing bacteria (SRB) to sulfides. The threshold of inhibition of sulfides, generally acknowledged to be toxic to biomass, in particular the methane producing bacteria (MPB), has been assumed to be 200-300 mg S2"/L [1]. The selectivity of various sulfate reducing bacteria and methane producing bacteria for energy substrates is quite varied. As shown in several recent studies, the spectrum of organics utilized by SRB's is much wider than in the case of methanogens [2-4]. This explains early successes in utilizing SRB's to accelerate anaerobic stabilization of sewage sludges [5,6]. More recently, the mixed-culture work of Middleton and Lawrence [7], DLA Inc. [8], Hilton et al. [9], Oleszkiewicz and Hilton [10,11], and Olthof et al. [12] have indicated substantial advantages of sulfidogenic pathways in application to high sulfate complex industrial waste streams. In the sulfidogenic pathways, organic matter is oxidized using sulfate as an electron acceptor in contrast to the conventional methanogenic pathway where C02 acts as an electron acceptor and where the volatile fatty acids are broken down to methane as an end product. Middleton and Lawrence [7], and Obayashi and Cork [13], using seed cultures obtained from anaerobic digesters, grew SRB's to the exclusion of methanogens, using acetate as the carbon source. In another study [14], the acetate consumption rate was shown to be 15-fold higher for SRB than for MPB's. Lovley et al. [15] found that the SRB's usually outcompete MPB due to lowering the partial pressure of hydrogen below levels that could effectively be utilized by MPB. Based upon those studies, one would expect that in the presence of fermentative bacteria forming short-chain fatty acids, especially lactate and acetate, SRB's would oxidize the lactate and acetate to carbon dioxide and water and would reduce sulfate to sulfide. In the process, one would expect that the methanogenic population either would be outcompeted for substrates or would be inhibited by the generated sulfide. PURPOSE AND SCOPE The purpose of this study was to maximize sulfate reduction using a minimal quantity of carbon. It was expected that the lactate formed during acidogenesis would first be incompletely oxidized to acetate and carbon dioxide by incomplete oxidizing SRB's then the remaining acetate would be completely oxidized to carbon dioxide by the complete oxidizing SRB's. In other words, it was expected that the mixed culture would consist of acidogenic anaerobes, incomplete oxidizing SRB's, and complete oxidizing SRB's. Continuous stripping of residual sulfides was operated to eliminate problems of transient inhibition. High sulfate loads, in excess of 1.0 g S6 + /L/d were accompanied by high carbon loads in excess of 1.5 g TOC/L/d in order to define the optimum conditions for sulfate reduction in terms of the carbon to sulfur (C/S) ratio in the feed and in terms of maximum organic loading (Bv) and sulfate-sulfur loading (L,) to the system. 156
Object Description
Purdue Identification Number | ETRIWC198618 |
Title | Anaerobic treatment of high strength, high sulfate wastes |
Author |
Hilton, Barry L. Oleszkiewicz, Jan A. |
Date of Original | 1986 |
Conference Title | Proceedings of the 41st Industrial Waste Conference |
Conference Front Matter (copy and paste) | http://e-archives.lib.purdue.edu/u?/engext,37786 |
Extent of Original | p. 156-166 |
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 | 2009-07-13 |
Capture Device | Fujitsu fi-5650C |
Capture Details | ScandAll 21 |
Resolution | 300 ppi |
Color Depth | 8 bit |
Description
Title | page 156 |
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 | 18 ANAEROBIC TREATMENT OF HIGH STRENGTH, HIGH SULFATE WASTES Barry L. Hilton, Research Assistant Jan A. Oleszkiewicz, Associate Professor Department of Civil Engineering The University of Manitoba Winnipeg, Manitoba Canada R3T 2N2 INTRODUCTION The high rate of accumulation of sulfates constitutes a growing environmental concern. Large quantities of sulfates are generated by the electric power industry from flue gas desulfurization sludges. The pulp and paper industry, pharmaceutical industry, and segments of the food industry produce effluents which are high in sulfates and other species of oxidized sulfur compounds. The application of methanogenic treatment processes to these wastes may be hindered by the resulting reduction of these oxidized sulfur species by sulfate reducing bacteria (SRB) to sulfides. The threshold of inhibition of sulfides, generally acknowledged to be toxic to biomass, in particular the methane producing bacteria (MPB), has been assumed to be 200-300 mg S2"/L [1]. The selectivity of various sulfate reducing bacteria and methane producing bacteria for energy substrates is quite varied. As shown in several recent studies, the spectrum of organics utilized by SRB's is much wider than in the case of methanogens [2-4]. This explains early successes in utilizing SRB's to accelerate anaerobic stabilization of sewage sludges [5,6]. More recently, the mixed-culture work of Middleton and Lawrence [7], DLA Inc. [8], Hilton et al. [9], Oleszkiewicz and Hilton [10,11], and Olthof et al. [12] have indicated substantial advantages of sulfidogenic pathways in application to high sulfate complex industrial waste streams. In the sulfidogenic pathways, organic matter is oxidized using sulfate as an electron acceptor in contrast to the conventional methanogenic pathway where C02 acts as an electron acceptor and where the volatile fatty acids are broken down to methane as an end product. Middleton and Lawrence [7], and Obayashi and Cork [13], using seed cultures obtained from anaerobic digesters, grew SRB's to the exclusion of methanogens, using acetate as the carbon source. In another study [14], the acetate consumption rate was shown to be 15-fold higher for SRB than for MPB's. Lovley et al. [15] found that the SRB's usually outcompete MPB due to lowering the partial pressure of hydrogen below levels that could effectively be utilized by MPB. Based upon those studies, one would expect that in the presence of fermentative bacteria forming short-chain fatty acids, especially lactate and acetate, SRB's would oxidize the lactate and acetate to carbon dioxide and water and would reduce sulfate to sulfide. In the process, one would expect that the methanogenic population either would be outcompeted for substrates or would be inhibited by the generated sulfide. PURPOSE AND SCOPE The purpose of this study was to maximize sulfate reduction using a minimal quantity of carbon. It was expected that the lactate formed during acidogenesis would first be incompletely oxidized to acetate and carbon dioxide by incomplete oxidizing SRB's then the remaining acetate would be completely oxidized to carbon dioxide by the complete oxidizing SRB's. In other words, it was expected that the mixed culture would consist of acidogenic anaerobes, incomplete oxidizing SRB's, and complete oxidizing SRB's. Continuous stripping of residual sulfides was operated to eliminate problems of transient inhibition. High sulfate loads, in excess of 1.0 g S6 + /L/d were accompanied by high carbon loads in excess of 1.5 g TOC/L/d in order to define the optimum conditions for sulfate reduction in terms of the carbon to sulfur (C/S) ratio in the feed and in terms of maximum organic loading (Bv) and sulfate-sulfur loading (L,) to the system. 156 |
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Color Depth | 8 bit |
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