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28 AEROBIC AND ANAEROBIC TREATMENT OF HIGH-STRENGTH INDUSTRIAL WASTE RESIDUES E. S. Venkataramani, Engineering Associate Merck & Co., Inc. Rahway, New Jersey 07065 Robert C. Ahlert, Professor II Rutgers, The State University of New Jersey Department of Chemical and Biochemical Engineering Piscataway, New Jersey 08854 Patricia Corbo, Engineer DuPont, Savannah River Works Aiken, South Carolina 29801 INTRODUCTION The pollution of groundwater by high-strength industrial waste residues, leaching from landfills, is relatively recent and adds a new dimension to existing pollution problems. Many landfills have inadvertently accepted chemical waste for disposal. Over a period of time, waste containers corrode and release solvents, oils, and synthetic chemicals, that constitute potential problems of enormous magnitude and complexity. The list of abandoned hazardous waste sites to be cleaned up under Superfund could grow to between 1500 and 2500 [1]. Possible contamination of groundwater by landfills is most serious in the Northeast. Depending on the wastes deposited at an industrial landfill site, the leachate produced can contain various synthetic and toxic chemicals, including heavy metals and known or suspected carcinogens [2]. Many represent classes of molecules that biologists and biochemists have not investigated previously. Shukrow et al. [3] obtained composition data on leacha- tes, contaminated aquifers, and surface waters in the proximity of twenty-seven sites containing hazardous wastes. Ghassemi et al. [4] developed a data base for thirty different leachates from eleven landfills. Hill et al. [5] investigated the relationships between BOD, COD, and TOC using a measurably larger data file in some industrial waste categories. An extensive discussion of biological treatment of high-strength leachates and industrial residues can be found in a review article by the authors [6]. Recently, Kosson developed an efficient, cost-effective, in-situ bio-reclamation technique for cleanup of hazardous leachates and soil contaminated with waste residues [7]. The present work was designed to establish that aerobic, as well as anaerobic, biological treatment can be used effectively to stabilize organic compounds found in high-strength waste residues. In the aerobic treatment step, an activated sludge biomass is used to develop microbial populations capable of metabolizing the organic compounds. A research scheme was designed to identify the mode of removal of synthetic organic compounds. The process kinetics were elucidated by following microbial responses to organic species in the high-strength waste. In the anaerobic treatment step, an anaerobic population was developed from an industrial seed acclimated to two feeds: 1) one containing the industrial residue; and 2) a second, synthetic feed simulating the volatile fatty acid content of the industrial residue. Seed cultures were maintained for nine months. The kinetics of volatile fatty acid uptake and methane production from industrial residue containing other contaminants were compared with those of the synthetic waste to assess the feasibility of application of anaerobic treatment for waste stabilization. MATERIALS AND METHODS High-Strength Industrial Waste Residue The high-strength, complex industrial landfill leachate used in these studies is the aqueous phase of a raw oil/water leachate mixture. This was provided by the USEPA Oil and Hazardous Materials Spills Branch (Edison, NJ). Some of the recognized industrial pollutants found to be present in this waste are illustrated by Table I [3]. Leachate samples designated as EPA-02, 04, and 07 were obtained 249
Object Description
Purdue Identification Number | ETRIWC198628 |
Title | Aerobic and anaerobic treatment of high-strength industrial waste residues |
Author |
Venkataramani, E. S. Ahlert, R. C., 1932- Corbo, Patricia |
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. 249-260 |
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 249 |
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 | 28 AEROBIC AND ANAEROBIC TREATMENT OF HIGH-STRENGTH INDUSTRIAL WASTE RESIDUES E. S. Venkataramani, Engineering Associate Merck & Co., Inc. Rahway, New Jersey 07065 Robert C. Ahlert, Professor II Rutgers, The State University of New Jersey Department of Chemical and Biochemical Engineering Piscataway, New Jersey 08854 Patricia Corbo, Engineer DuPont, Savannah River Works Aiken, South Carolina 29801 INTRODUCTION The pollution of groundwater by high-strength industrial waste residues, leaching from landfills, is relatively recent and adds a new dimension to existing pollution problems. Many landfills have inadvertently accepted chemical waste for disposal. Over a period of time, waste containers corrode and release solvents, oils, and synthetic chemicals, that constitute potential problems of enormous magnitude and complexity. The list of abandoned hazardous waste sites to be cleaned up under Superfund could grow to between 1500 and 2500 [1]. Possible contamination of groundwater by landfills is most serious in the Northeast. Depending on the wastes deposited at an industrial landfill site, the leachate produced can contain various synthetic and toxic chemicals, including heavy metals and known or suspected carcinogens [2]. Many represent classes of molecules that biologists and biochemists have not investigated previously. Shukrow et al. [3] obtained composition data on leacha- tes, contaminated aquifers, and surface waters in the proximity of twenty-seven sites containing hazardous wastes. Ghassemi et al. [4] developed a data base for thirty different leachates from eleven landfills. Hill et al. [5] investigated the relationships between BOD, COD, and TOC using a measurably larger data file in some industrial waste categories. An extensive discussion of biological treatment of high-strength leachates and industrial residues can be found in a review article by the authors [6]. Recently, Kosson developed an efficient, cost-effective, in-situ bio-reclamation technique for cleanup of hazardous leachates and soil contaminated with waste residues [7]. The present work was designed to establish that aerobic, as well as anaerobic, biological treatment can be used effectively to stabilize organic compounds found in high-strength waste residues. In the aerobic treatment step, an activated sludge biomass is used to develop microbial populations capable of metabolizing the organic compounds. A research scheme was designed to identify the mode of removal of synthetic organic compounds. The process kinetics were elucidated by following microbial responses to organic species in the high-strength waste. In the anaerobic treatment step, an anaerobic population was developed from an industrial seed acclimated to two feeds: 1) one containing the industrial residue; and 2) a second, synthetic feed simulating the volatile fatty acid content of the industrial residue. Seed cultures were maintained for nine months. The kinetics of volatile fatty acid uptake and methane production from industrial residue containing other contaminants were compared with those of the synthetic waste to assess the feasibility of application of anaerobic treatment for waste stabilization. MATERIALS AND METHODS High-Strength Industrial Waste Residue The high-strength, complex industrial landfill leachate used in these studies is the aqueous phase of a raw oil/water leachate mixture. This was provided by the USEPA Oil and Hazardous Materials Spills Branch (Edison, NJ). Some of the recognized industrial pollutants found to be present in this waste are illustrated by Table I [3]. Leachate samples designated as EPA-02, 04, and 07 were obtained 249 |
Resolution | 300 ppi |
Color Depth | 8 bit |
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