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Section Six PLATING WASTES 55 IRON PROCESS FOR TREATMENT OF Cr(VI) WASTEWATERS Alan R. Bowers, Assistant Professor Carlos A. Ortiz, Graduate Student Roberto J. Cardozo, Graduate Student Department of Civil and Environmental Engineering Vanderbilt University Nashville, Tennessee 37235 INTRODUCTION The technology for treatment of Cr(VI)-bearing wastewaters has been well established. Conventional methods are based on the reduction of Cr(VI) to Cr(lII) followed by precipitation as Cr(OH)3 at high pH, ca. 8.0 to 10.0 [1-11]. Although other techniques such as ion exchange and activated carbon adsorption have been successfully demonstrated in the laboratory, they have not been employed to any significant degree in full-scale operations [12-15]. A variety of reducing agents have been suggested for Cr(VI) reduction,including sulfides, bisulfites, metabisulfites, ferrous sulfate, and sulfur dioxide [1,7,8,11]. Although quite effective as reducing agents, the cost of these chemicals may not be entirely justified due to the availability of equally effective waste materials, such as scrap iron, for the reduction of Cr(VI). Furthermore, the cost of reducing Cr(VI) with conventional chemicals is greatly increased by side reactions with dissolved oxygen, which is ubiquitous in aqueous systems that are in contact with the atmosphere [16, 17]. Typically, the chemical dosage needed for Cr(VI) reduction is two times the stoichiometric requirement [11,16]. Based on this ratio, a comparison of chemical costs for Cr(VI) reduction is shown in Table I. The costs shown in Table I indicate that scrap iron has the potential to be significantly more economical than conventional means of Cr(VI) reduction, e.g., > 10 times cheaper than the least expensive alternative. In addition, the iron solubilized by oxidation may act as a conditioning agent for the resulting Cr(OH)3 sludge and, thus, produce a greater overall benefit in cost that would not be Table I. Cost Comparison of Chromium (VI) Reducing Agents Chemical Costs" Reducing Agent ($/Kg Cr) S02 0.85" NaHSO, 1.15c FeS 3.33d FeS04 1.25' Scrap Iron 0.05f(0.08) "Costs calculated assuming required dosage equal to 2 times the stoichiometric requirement!11]. °$210/ton for S02 [20]. c$0.174/lbfor NaHSOj [20]. d$0.45/Ib for FeS [20]. '$130/ton for FeS04 [20]. f$l.00/100 lb for scrap iron, current market price in Nashville, TN., based on telephone survey of local dealers, August, 1985. Value in parenthesis represents 3.5 times the stoichiometric requirement as found necessary in this work. 465
Object Description
Purdue Identification Number | ETRIWC198655 |
Title | Iron process for treatment of Cr(VI) wastewaters |
Author |
Bowers, Alan R. Ortiz, Carlos A. Cardozo, Roberto J. |
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. 465-473 |
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 465 |
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 | Section Six PLATING WASTES 55 IRON PROCESS FOR TREATMENT OF Cr(VI) WASTEWATERS Alan R. Bowers, Assistant Professor Carlos A. Ortiz, Graduate Student Roberto J. Cardozo, Graduate Student Department of Civil and Environmental Engineering Vanderbilt University Nashville, Tennessee 37235 INTRODUCTION The technology for treatment of Cr(VI)-bearing wastewaters has been well established. Conventional methods are based on the reduction of Cr(VI) to Cr(lII) followed by precipitation as Cr(OH)3 at high pH, ca. 8.0 to 10.0 [1-11]. Although other techniques such as ion exchange and activated carbon adsorption have been successfully demonstrated in the laboratory, they have not been employed to any significant degree in full-scale operations [12-15]. A variety of reducing agents have been suggested for Cr(VI) reduction,including sulfides, bisulfites, metabisulfites, ferrous sulfate, and sulfur dioxide [1,7,8,11]. Although quite effective as reducing agents, the cost of these chemicals may not be entirely justified due to the availability of equally effective waste materials, such as scrap iron, for the reduction of Cr(VI). Furthermore, the cost of reducing Cr(VI) with conventional chemicals is greatly increased by side reactions with dissolved oxygen, which is ubiquitous in aqueous systems that are in contact with the atmosphere [16, 17]. Typically, the chemical dosage needed for Cr(VI) reduction is two times the stoichiometric requirement [11,16]. Based on this ratio, a comparison of chemical costs for Cr(VI) reduction is shown in Table I. The costs shown in Table I indicate that scrap iron has the potential to be significantly more economical than conventional means of Cr(VI) reduction, e.g., > 10 times cheaper than the least expensive alternative. In addition, the iron solubilized by oxidation may act as a conditioning agent for the resulting Cr(OH)3 sludge and, thus, produce a greater overall benefit in cost that would not be Table I. Cost Comparison of Chromium (VI) Reducing Agents Chemical Costs" Reducing Agent ($/Kg Cr) S02 0.85" NaHSO, 1.15c FeS 3.33d FeS04 1.25' Scrap Iron 0.05f(0.08) "Costs calculated assuming required dosage equal to 2 times the stoichiometric requirement!11]. °$210/ton for S02 [20]. c$0.174/lbfor NaHSOj [20]. d$0.45/Ib for FeS [20]. '$130/ton for FeS04 [20]. f$l.00/100 lb for scrap iron, current market price in Nashville, TN., based on telephone survey of local dealers, August, 1985. Value in parenthesis represents 3.5 times the stoichiometric requirement as found necessary in this work. 465 |
Resolution | 300 ppi |
Color Depth | 8 bit |
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