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DEVELOPMENT OF A BIOLOGICAL DENITRIFICATION PROCESS FOR A HIGH-STRENGTH INDUSTRIAL WASTE Cyron T. Lawson, Developmental Scientist Research and Development Department Union Carbide Corporation South Charleston, West Virginia 25303 The addition of a new manufacturing unit under consideration for one of Union Carbide's plants would result in a particularly high-strength aqueous waste. At the developmental stage, the waste composition was defined, in terms of conventional wastewater parameters: • BODs = 34,000-63,000 mg/1 •COD = 135,000-240,000 mg/1 • TOC = 26,000-55,000 mg/1 •N03-N= 9,600-12,000 mg (as N)/l in terms of specific chemicals: •NaN03 = 6-10.7% by wt. • Alcohols, glycols, sodium salts, and polyglycols = 5.3-11.0% by wt. • Other organics = 1.0-2.1% by wt. " pH = 3.0-5.6 or "^ 12.0 (depending on final process equipment design) At the anticipated process waste flow, the daily organic load from the process would be about equal to the existing raw waste load from all other sources at the existing plant site chosen for process installation. The new process could constitute a serious treatment plant overload. Furthermore, the nitrate content required treatment to meet an anticipated discharge limite of 20-25 mg NO3-N/I in the effluent (about 100 mg/1 of NOJ ion). Literature reviews and consultation with personnel at the Oak Ridge National Laboratory [1-3] showed that anaerobic biological denitrification had considerable potential for simultaneously removing both the nitrates and a large fraction of the organics from this process waste. In fact, a full-scale denitrification facility was in operation at the Oak Ridge Y-12 Plant [3). Whde ORNL researchers had demonstrated successful denitrification processes in both stirred reactors (analogous to the aerobic activated sludge process) and packed-bed reactors, we chose to pursue the stirred reactor configuration for three reasons. 1. Since the packed-bed process had not yet been demonstrated on a large scale, many scale-up questions remained. 2. With the process waste not yet well-defined, and potentially quite variable in composition, the completely mixed stirred reactor seemed to offer more inherent process stability. 3. Biomass management in a packed-bed treating a high-strength waste at high reaction rates, with a potential for sloughing of excess bio-growth, seemed to be a particularly troublesome consideration at full-scale operation. DEVELOPMENT OF THE DENITRIFICATION PROCESS Biological Culture Development Dr. Alicia Compere and Dr. William Griffiths at ORNL were very helpful in providing frozen cultures of denitrifiers and in defining optimum culturing procedures. Because of 882
Object Description
Purdue Identification Number | ETRIWC198087 |
Title | Development of a biological denitrification process for a high-strength industrial waste |
Author |
Lawson, Cyron T. |
Date of Original | 1980 |
Conference Title | Proceedings of the 35th Industrial Waste Conference |
Extent of Original | p. 882-888 |
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 | 2009-10-22 |
Capture Device | Fujitsu fi-5650C |
Capture Details | ScandAll 21 |
Resolution | 300 ppi |
Color Depth | 8 bit |
Description
Title | page 882 |
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 | DEVELOPMENT OF A BIOLOGICAL DENITRIFICATION PROCESS FOR A HIGH-STRENGTH INDUSTRIAL WASTE Cyron T. Lawson, Developmental Scientist Research and Development Department Union Carbide Corporation South Charleston, West Virginia 25303 The addition of a new manufacturing unit under consideration for one of Union Carbide's plants would result in a particularly high-strength aqueous waste. At the developmental stage, the waste composition was defined, in terms of conventional wastewater parameters: • BODs = 34,000-63,000 mg/1 •COD = 135,000-240,000 mg/1 • TOC = 26,000-55,000 mg/1 •N03-N= 9,600-12,000 mg (as N)/l in terms of specific chemicals: •NaN03 = 6-10.7% by wt. • Alcohols, glycols, sodium salts, and polyglycols = 5.3-11.0% by wt. • Other organics = 1.0-2.1% by wt. " pH = 3.0-5.6 or "^ 12.0 (depending on final process equipment design) At the anticipated process waste flow, the daily organic load from the process would be about equal to the existing raw waste load from all other sources at the existing plant site chosen for process installation. The new process could constitute a serious treatment plant overload. Furthermore, the nitrate content required treatment to meet an anticipated discharge limite of 20-25 mg NO3-N/I in the effluent (about 100 mg/1 of NOJ ion). Literature reviews and consultation with personnel at the Oak Ridge National Laboratory [1-3] showed that anaerobic biological denitrification had considerable potential for simultaneously removing both the nitrates and a large fraction of the organics from this process waste. In fact, a full-scale denitrification facility was in operation at the Oak Ridge Y-12 Plant [3). Whde ORNL researchers had demonstrated successful denitrification processes in both stirred reactors (analogous to the aerobic activated sludge process) and packed-bed reactors, we chose to pursue the stirred reactor configuration for three reasons. 1. Since the packed-bed process had not yet been demonstrated on a large scale, many scale-up questions remained. 2. With the process waste not yet well-defined, and potentially quite variable in composition, the completely mixed stirred reactor seemed to offer more inherent process stability. 3. Biomass management in a packed-bed treating a high-strength waste at high reaction rates, with a potential for sloughing of excess bio-growth, seemed to be a particularly troublesome consideration at full-scale operation. DEVELOPMENT OF THE DENITRIFICATION PROCESS Biological Culture Development Dr. Alicia Compere and Dr. William Griffiths at ORNL were very helpful in providing frozen cultures of denitrifiers and in defining optimum culturing procedures. Because of 882 |
Resolution | 300 ppi |
Color Depth | 8 bit |
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