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REMOVAL OF CYANIDES FROM COKE PLANT WASTEWATERS BY SELECTIVE ION EXCHANGE-RESULTS OF PILOT TESTING PROGRAM Robert A. Bessent, Environmental Engineer Paul A. Luther, Senior Environmental Engineer Carl W. Eklund, Associate Envirodyne Engineers 12161 Lackland Road St. Louis, Missouri 63141 INTRODUCTION Selective ion exchange treatment technology was chosen to remove cyanides from coke plant wastewaters at a midwest steel manufacturer. Due to limited information on the effectiveness of ion exchange treatment technology to coke plant wastewaters, a pilot study was conducted to determine its applicability. Cyanide limitations to be met by a full-scale ion exchange treatment system effluent, as dictated by the receiving metropolitan sewage authority, are 2 mg/1 free cyanide and 10 mg/1 total cyanide. In addition to cyanide limitations, total iron is limited to 50 mg/1. The pilot study program was initiated based on the information outlined by Avert and Waitz [1], This paper presents the results of a pilot program based upon selective ion exchange treatment of complex cyanides. Preliminary design parameters and flow diagrams resulting from the pilot study are also presented. PROCESS DESCRIPTION Rohm and Haas Amberlite IRA 958 (formerly XE-279) ion exchange resin was chosen for its ability to specifically remove complexed cyanides present in the coke plant wastewater. Amberlite IRA 958 resin is made of an acrylic material and is a strongly basic anionic exchanger with a published capacity ranging between 1.2 to 2.3 pounds of complexed cyanide per cubic foot [1]. Free cyanides are not effectively removed by the resin; therefore, ferrous sulfate is added to the coke plant wastewater to convert free cyanides to ferrocyanides. Ferrocyanides can then be removed in the ion exchange columns. The equation for the conversion of free cyanide to ferrocyanide is [1]: Fe2+ + 6CN" P10^9 FefCN)t 0) Under alkaline conditions, excess iron introduced to this reaction precipitates as ferrous hydroxide. The Fe(OH)2 precipitate, conditioned by cationic and anionic polymers, is settled following a flocculation period. Insoluble complex cyanides also settle out during this operation. The clarified coke plant wastewater proceeds to a filtration system followed by the ion exchange columns. The purpose of the filtration system is to protect the resin in the ion exchange columns from excess solids carried over from the clarifier. The ion exchange columns remove cyanides as follows [ 1 ]: 4 Resin-N-R3+cr + Fe(CN)«~ -» (Resin-N-R3+)4 + (Fe(CN)J") + 4Cl~ (2) Once the ion exchange resin is exhausted, it is regenerated with a 15% solution of NaCl [ 1 ]: (Resin-N-R3)4 + (FefCN/e" ) + 4NaCl -+4 Resin-N-R3+Cr+ Na4Fe(CN)6 (3) The regenerant stream contains a less toxic concentrated form of cyanide which will be treated by ultraviolet ozonation. After adequate regeneration, the exchange resin is rinsed with water, and then backwashed for reclassification and cleansing purposes. Coke plant wastewater can then be reintroduced to the ion exchange column to begin a new treatment cycle. 47
Object Description
Purdue Identification Number | ETRIWC197906 |
Title | Removal of cyanides from coke plant wastewaters by selective ion exchange : results of pilot testing program |
Author |
Bessent, Robert A. Luther, P. A. (Paul A.) Eklund, Carl |
Date of Original | 1979 |
Conference Title | Proceedings of the 34th Industrial Waste Conference |
Conference Front Matter (copy and paste) | http://earchives.lib.purdue.edu/u?/engext,30453 |
Extent of Original | p. 47-62 |
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 | 2009-06-24 |
Capture Device | Fujitsu fi-5650C |
Capture Details | ScandAll 21 |
Resolution | 300 ppi |
Color Depth | 8 bit |
Description
Title | page0047 |
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 | REMOVAL OF CYANIDES FROM COKE PLANT WASTEWATERS BY SELECTIVE ION EXCHANGE-RESULTS OF PILOT TESTING PROGRAM Robert A. Bessent, Environmental Engineer Paul A. Luther, Senior Environmental Engineer Carl W. Eklund, Associate Envirodyne Engineers 12161 Lackland Road St. Louis, Missouri 63141 INTRODUCTION Selective ion exchange treatment technology was chosen to remove cyanides from coke plant wastewaters at a midwest steel manufacturer. Due to limited information on the effectiveness of ion exchange treatment technology to coke plant wastewaters, a pilot study was conducted to determine its applicability. Cyanide limitations to be met by a full-scale ion exchange treatment system effluent, as dictated by the receiving metropolitan sewage authority, are 2 mg/1 free cyanide and 10 mg/1 total cyanide. In addition to cyanide limitations, total iron is limited to 50 mg/1. The pilot study program was initiated based on the information outlined by Avert and Waitz [1], This paper presents the results of a pilot program based upon selective ion exchange treatment of complex cyanides. Preliminary design parameters and flow diagrams resulting from the pilot study are also presented. PROCESS DESCRIPTION Rohm and Haas Amberlite IRA 958 (formerly XE-279) ion exchange resin was chosen for its ability to specifically remove complexed cyanides present in the coke plant wastewater. Amberlite IRA 958 resin is made of an acrylic material and is a strongly basic anionic exchanger with a published capacity ranging between 1.2 to 2.3 pounds of complexed cyanide per cubic foot [1]. Free cyanides are not effectively removed by the resin; therefore, ferrous sulfate is added to the coke plant wastewater to convert free cyanides to ferrocyanides. Ferrocyanides can then be removed in the ion exchange columns. The equation for the conversion of free cyanide to ferrocyanide is [1]: Fe2+ + 6CN" P10^9 FefCN)t 0) Under alkaline conditions, excess iron introduced to this reaction precipitates as ferrous hydroxide. The Fe(OH)2 precipitate, conditioned by cationic and anionic polymers, is settled following a flocculation period. Insoluble complex cyanides also settle out during this operation. The clarified coke plant wastewater proceeds to a filtration system followed by the ion exchange columns. The purpose of the filtration system is to protect the resin in the ion exchange columns from excess solids carried over from the clarifier. The ion exchange columns remove cyanides as follows [ 1 ]: 4 Resin-N-R3+cr + Fe(CN)«~ -» (Resin-N-R3+)4 + (Fe(CN)J") + 4Cl~ (2) Once the ion exchange resin is exhausted, it is regenerated with a 15% solution of NaCl [ 1 ]: (Resin-N-R3)4 + (FefCN/e" ) + 4NaCl -+4 Resin-N-R3+Cr+ Na4Fe(CN)6 (3) The regenerant stream contains a less toxic concentrated form of cyanide which will be treated by ultraviolet ozonation. After adequate regeneration, the exchange resin is rinsed with water, and then backwashed for reclassification and cleansing purposes. Coke plant wastewater can then be reintroduced to the ion exchange column to begin a new treatment cycle. 47 |
Resolution | 300 ppi |
Color Depth | 8 bit |
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