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Section 7. PAINT, INK, AND DYE WASTES BIOLOGICAL TREATMENT OF PHENOLIC PAINT-STRIPPING WASTEWATER Capt. Jack H. Jeter, Research Environmental Engineer HQ Air Force Engineering and Services Center Tyndall Air Force Base, Florida INTRODUCTION Paint-stripping operations for control of corrosion on aircraft are performed at practically all Air Force bases. There are primarily two operations used for stripping the aircraft, spray operations and dip tank operations. Aircraft parts are either sprayed with the paint stripper, or dipped into large tanks containing stripper. The parts are then rinsed with large quantities of water. Both of these operations generate large quantities of wastewater with high concentrations of organic pollutants. Between 20,000 and 200,000 gallons of stripper laden wastewater are generated for each aircraft stripped [1]. The coatings used on aircraft are required to be very resistant to abrasion, and are therefore very hard to remove. They usually consist of the epoxy primers with polyurethane topcoats. These coatings are very resistant to chemical strippers and require the most aggressive strippers. Strippers with 20% phenol as the active ingredient are the most effective on these epoxy/polyurethane coatings. An additive of considerable environmental concern in the stripper solution is hexavalent chromium. The resultant wastewater, high in phenol and chromium due to the chemical stripper, is further contaminated by the chromate constituents in the paints, i.e., zinc chromate and strontium chromate. The Air Force has centralized the large paint-stripping and other industrial operations into Air Logistics Centers (ALC). The paint-stripping operations are performed intermittently. The treatment of the wastewaters generated on these ALC's is a problem due to a number of factors: the variability of the flow rates from the stripping facilities, the variation in the concentrations of the toxic organic components, and the toxic or inhibitory action of the phenolic compounds. The purpose of this paper is to describe a method developed for biological treatment of paint- stripping wastewaters. AIR FORCE OFFICE OF SCIENTIFIC RESEARCH/TRINITY UNIVERSITY PROJECT, "AN ECOLOGICAL APPROACH TO THE PROBLEM OF BIODEGRADATION OF PHENOLIC WASTES" Under a grant from the Air Force, Trinity University in San Antonio, Texas studied the population ecology and stability of microorganisms involved in the biodegradation of phenolic compounds. In the early 70's the paint strippers most commonly used by the military consisted of approximately 53% dichlorobenzene, 25% cresol, and 22% paraffin, etc. The purpose of this research was to investigate the reasons for the failure of biological treatment plants which receive phenolic paint stripping wastewater. The investigators obtained organisms from the paint-stripping facility in San Antonio in areas exposed to the paint-stripping wastewater. Organisms were also collected from the waste treatment trickling filter. The cresol-degrading organisms were isolated on agar plates of mineral salts media with 900 mg/1 cresol as the sole carbon and energy source. The organisms initially isolated included Pseudomonas aeruginosa, P. fluorescens, and P. putida. The isolated cresol degraders were grown in synthetic wastewater, liquid mineral salts media containing 900 mg/1 cresol, and seeded onto a glass column, 6 inch diameter and 9 feet tall, containing a ceramic saddle packing medium. The organisms rapidly colonized the packing medium. The experimental parameters investigated for their effect on cresol utilization included temper- 159
Object Description
Purdue Identification Number | ETRIWC198517 |
Title | Biological treatment of phenolic paint-stripping wastewater |
Author | Jeter, Jack H. |
Date of Original | 1985 |
Conference Title | Proceedings of the 40th Industrial Waste Conference |
Conference Front Matter (copy and paste) | http://e-archives.lib.purdue.edu/u?/engext,36131 |
Extent of Original | p. 159-164 |
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 | 2009-07-14 |
Capture Device | Fujitsu fi-5650C |
Capture Details | ScandAll 21 |
Resolution | 300 ppi |
Color Depth | 8 bit |
Description
Title | page 159 |
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 7. PAINT, INK, AND DYE WASTES BIOLOGICAL TREATMENT OF PHENOLIC PAINT-STRIPPING WASTEWATER Capt. Jack H. Jeter, Research Environmental Engineer HQ Air Force Engineering and Services Center Tyndall Air Force Base, Florida INTRODUCTION Paint-stripping operations for control of corrosion on aircraft are performed at practically all Air Force bases. There are primarily two operations used for stripping the aircraft, spray operations and dip tank operations. Aircraft parts are either sprayed with the paint stripper, or dipped into large tanks containing stripper. The parts are then rinsed with large quantities of water. Both of these operations generate large quantities of wastewater with high concentrations of organic pollutants. Between 20,000 and 200,000 gallons of stripper laden wastewater are generated for each aircraft stripped [1]. The coatings used on aircraft are required to be very resistant to abrasion, and are therefore very hard to remove. They usually consist of the epoxy primers with polyurethane topcoats. These coatings are very resistant to chemical strippers and require the most aggressive strippers. Strippers with 20% phenol as the active ingredient are the most effective on these epoxy/polyurethane coatings. An additive of considerable environmental concern in the stripper solution is hexavalent chromium. The resultant wastewater, high in phenol and chromium due to the chemical stripper, is further contaminated by the chromate constituents in the paints, i.e., zinc chromate and strontium chromate. The Air Force has centralized the large paint-stripping and other industrial operations into Air Logistics Centers (ALC). The paint-stripping operations are performed intermittently. The treatment of the wastewaters generated on these ALC's is a problem due to a number of factors: the variability of the flow rates from the stripping facilities, the variation in the concentrations of the toxic organic components, and the toxic or inhibitory action of the phenolic compounds. The purpose of this paper is to describe a method developed for biological treatment of paint- stripping wastewaters. AIR FORCE OFFICE OF SCIENTIFIC RESEARCH/TRINITY UNIVERSITY PROJECT, "AN ECOLOGICAL APPROACH TO THE PROBLEM OF BIODEGRADATION OF PHENOLIC WASTES" Under a grant from the Air Force, Trinity University in San Antonio, Texas studied the population ecology and stability of microorganisms involved in the biodegradation of phenolic compounds. In the early 70's the paint strippers most commonly used by the military consisted of approximately 53% dichlorobenzene, 25% cresol, and 22% paraffin, etc. The purpose of this research was to investigate the reasons for the failure of biological treatment plants which receive phenolic paint stripping wastewater. The investigators obtained organisms from the paint-stripping facility in San Antonio in areas exposed to the paint-stripping wastewater. Organisms were also collected from the waste treatment trickling filter. The cresol-degrading organisms were isolated on agar plates of mineral salts media with 900 mg/1 cresol as the sole carbon and energy source. The organisms initially isolated included Pseudomonas aeruginosa, P. fluorescens, and P. putida. The isolated cresol degraders were grown in synthetic wastewater, liquid mineral salts media containing 900 mg/1 cresol, and seeded onto a glass column, 6 inch diameter and 9 feet tall, containing a ceramic saddle packing medium. The organisms rapidly colonized the packing medium. The experimental parameters investigated for their effect on cresol utilization included temper- 159 |
Resolution | 300 ppi |
Color Depth | 8 bit |
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