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70 AZO DYES' METABOLISM BY PSEUDOMONAS PUTIDA Ajit K. Ghorpade, Senior Engineer, Merck & Co., Inc. Elkton, Virginia 22827 Hugh T. Spencer, Professor Department of Chemical Engineering University of Louisville Louisville, Kentucky 40292 INTRODUCTION Azo dyes are used extensively in textile and leather dyeing operations and contribute to problems associated with disposal of the wastewater generated from these operations. Generally, these waters contain high concentrations of sodium chloride and are brightly colored. Regulations controlling release of these effluents to Publicly Owned Treatment Works (POTWs) vary from state to state; however, regulators will decrease discharge limits on total residual chlorine and color of treated effluent. At present, sodium chloride and color concentrations in typical dye waste streams are 2,000 to 3,000 mg/L and 1,000 to 1,500 American Dye Manufacturer's Index (ADMI) units, respectively. Textile and leather dyes are, by design, built to resist degradation in the open environment. This keeps a dyed product usable for a longer period, but it also makes the treatment of dye waste more difficult; the same properties which help the dye to hold up to repeated washings also make it resistant to degradation in the wastewater treatment plant. At present, the industries facing this problem have found it possible to meet the color regulations by hyper-chlorination (chlorination beyond that needed for simple disinfection). Because of the anticipated change in residual chlorine regulation, textile industries will be looking for alternative ways to treat their dye waste. One such alternative will be to use designer organisms created to degrade azo dyes. Bacteria metabolizing the food materials in a wastewater stream tend to degrade first those substrates which have a biological origin and are in high concentration. Azo dyes are xenobiotics, compounds which do not have a biological origin. Therefore, a low azo dye concentration contained in textile wastewaters alone cannot be a source for bacterial growth. This study evaluates the extent of bacterial degradation of azo dye when using another substrate as a primary food and energy source. The bacterium, Pseudomonas putida, PRS 2015 with pAC 27, 3 Cba + , a genetically altered strain, was used to degrade three azo dyes in a chemostatic setting using 3-chlorobenzoic acid as a primary substrate. LITERATURE REVIEW Sulfonated azo dyes are produced and used in textile dyeing. They are xenobiotics since aromatic azo groups are not synthesized in the biosphere. As a consequence, they are recalcitrant in aerobic wastewater treatment. Hence, there is a major scientific interest in isolating microorganisms from nature capable of utilizing azo dyes as a sole carbon source. Most of the prior studies used oxygen as an electron acceptor and were aerobic. The anaerobic studies1"3 that used an electron acceptor other than oxygen will not be discussed in this paper. A summary of aerobic investigations is presented below, divided based on the nature of bacterial systems used during the experiments (i.e., mixed or pure culture). Azo Dyes Biodegradation by Mixed Cultures The studies in this class used sludge from POTWs or textile mill outfalls. Urushigawa and Yone- zawa developed an understanding of the relationship between the biodegradability of azo compounds and their molecular structures.4 The experiments were performed in Erlenmeyer flasks; the sludge and dye concentration used in the study were 1000 mg/L and 50 mg/L, respectively. The azo dye concentrations were determined by measuring UV absorbance of the centrifuged broth. The azo dyes studied 48th Purdue Industrial Waste Conference Proceedings, 1993 Lewis Publishers, Chelsea, Michigan 48118. Primed in U.S.A. 699
Object Description
Purdue Identification Number | ETRIWC199370 |
Title | Azo dyes' metabolism by Pseudomonas putida |
Author |
Ghorpade, Ajit K. Spencer, Hugh T. |
Date of Original | 1993 |
Conference Title | Proceedings of the 48th Industrial Waste Conference |
Conference Front Matter (copy and paste) | http://earchives.lib.purdue.edu/u?/engext,21159 |
Extent of Original | p. 669-714 |
Collection Title | Engineering Technical Reports Collection, Purdue University |
Repository | Purdue University Libraries |
Rights Statement | Digital object copyright Purdue University. All rights reserved. |
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Description
Title | page 699 |
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 | 70 AZO DYES' METABOLISM BY PSEUDOMONAS PUTIDA Ajit K. Ghorpade, Senior Engineer, Merck & Co., Inc. Elkton, Virginia 22827 Hugh T. Spencer, Professor Department of Chemical Engineering University of Louisville Louisville, Kentucky 40292 INTRODUCTION Azo dyes are used extensively in textile and leather dyeing operations and contribute to problems associated with disposal of the wastewater generated from these operations. Generally, these waters contain high concentrations of sodium chloride and are brightly colored. Regulations controlling release of these effluents to Publicly Owned Treatment Works (POTWs) vary from state to state; however, regulators will decrease discharge limits on total residual chlorine and color of treated effluent. At present, sodium chloride and color concentrations in typical dye waste streams are 2,000 to 3,000 mg/L and 1,000 to 1,500 American Dye Manufacturer's Index (ADMI) units, respectively. Textile and leather dyes are, by design, built to resist degradation in the open environment. This keeps a dyed product usable for a longer period, but it also makes the treatment of dye waste more difficult; the same properties which help the dye to hold up to repeated washings also make it resistant to degradation in the wastewater treatment plant. At present, the industries facing this problem have found it possible to meet the color regulations by hyper-chlorination (chlorination beyond that needed for simple disinfection). Because of the anticipated change in residual chlorine regulation, textile industries will be looking for alternative ways to treat their dye waste. One such alternative will be to use designer organisms created to degrade azo dyes. Bacteria metabolizing the food materials in a wastewater stream tend to degrade first those substrates which have a biological origin and are in high concentration. Azo dyes are xenobiotics, compounds which do not have a biological origin. Therefore, a low azo dye concentration contained in textile wastewaters alone cannot be a source for bacterial growth. This study evaluates the extent of bacterial degradation of azo dye when using another substrate as a primary food and energy source. The bacterium, Pseudomonas putida, PRS 2015 with pAC 27, 3 Cba + , a genetically altered strain, was used to degrade three azo dyes in a chemostatic setting using 3-chlorobenzoic acid as a primary substrate. LITERATURE REVIEW Sulfonated azo dyes are produced and used in textile dyeing. They are xenobiotics since aromatic azo groups are not synthesized in the biosphere. As a consequence, they are recalcitrant in aerobic wastewater treatment. Hence, there is a major scientific interest in isolating microorganisms from nature capable of utilizing azo dyes as a sole carbon source. Most of the prior studies used oxygen as an electron acceptor and were aerobic. The anaerobic studies1"3 that used an electron acceptor other than oxygen will not be discussed in this paper. A summary of aerobic investigations is presented below, divided based on the nature of bacterial systems used during the experiments (i.e., mixed or pure culture). Azo Dyes Biodegradation by Mixed Cultures The studies in this class used sludge from POTWs or textile mill outfalls. Urushigawa and Yone- zawa developed an understanding of the relationship between the biodegradability of azo compounds and their molecular structures.4 The experiments were performed in Erlenmeyer flasks; the sludge and dye concentration used in the study were 1000 mg/L and 50 mg/L, respectively. The azo dye concentrations were determined by measuring UV absorbance of the centrifuged broth. The azo dyes studied 48th Purdue Industrial Waste Conference Proceedings, 1993 Lewis Publishers, Chelsea, Michigan 48118. Primed in U.S.A. 699 |
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Color Depth | 8 bit |
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