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Section Eight LANDFILLS-B. LEACHATES 70 EVALUATION OF A FULL-SCALE PHYSICO-CHEMICAL TREATMENT PLANT FOR REMOVAL OF BDAT CONSTITUENTS FROM HAZARDOUS WASTE LANDFILL LEACHATE Bill Y. M. Liu, Project Engineer Alan Li, Project Manager Michael P. Henry, Project Manager Chemical Waste Management, Inc. Research and Development Geneva, Illinois 60134 Bruce Kruckel, Operational Manager Chemical Waste Management, Inc. Model City, New York 14107 INTRODUCTION Leachate, generated by water percolating through landfills, can be classified into the two broad categories: non-hazardous and hazardous leachates. Basically, hazardous leachate is generated from hazardous waste or co-disposal landfills, whereas non-hazardous leachate is generated from hazardous waste or co-disposal landfills, whereas non-hazardous leachate is defined as leachate from non- hazardous solid waste landfills. Because of the high concentrations of contaminants in leachate, leachate is generally treated before it can be discharged or disposed of.1 Both types of leachate can be treated with conventional wastewater treatment technologies, such as biological treatment for organic removal, metal precipitation for metal removal and granular activated carbon (GAC) adsorption for effluent polishing.1 The effluent from these leachate treatment plants usually discharges into Publically Owned Treatment Works (POTWs) or to surface waters under state or federal National Pollution Discharge Elimination System (NPDES) permits. The treatment residues are then disposed of in a hazardous landfill for hazardous treatment residues and a solid waste landfill for non-hazardous residues. However, the treatment practice for hazardous waste leachate will be significantly impacted and might have to change when the EPA promulgates the Third-Third landban regulation regarding multi-source leachate on May 8, 1990. The EPA has set on overall schedule for the land disposal program, which requires all land disposal restriction regulations to be in place by May 8, 1990.2 The EPA divided listed hazardous wastes into three groups (the "Third"), to be regulated in successive stages over a period of 66 months. The multi- source hazardous leachates, regulated by the Third Third, will have to meet the treatment standards for wastewaters and non-wastewaters before land disposal.3 The EPA developed the standards representing the best demonstrated available technology (BDAT). The BDAT constituents, totalling 231 compounds, include volatile organics (63 constituents) and semi-volatile organics (107 constituents), metals (16 constituents), inorganics other than metals (3 constituents), organochlorine pesticides (20 constituents), phenoxyacetic acid herbicides (3 constituents), organophosphorus insecticides (5 constituents), polychlorinated biphenyls (7 constituents) and dioxins and furans (7 constituents). In the proposed rule for the Third Third landban2, leachate has to meet the wastewater standard, consisting of 228 BDAT compounds, before land disposal in the surface impoundment. Treatment residues, such as metal and biological sludges from the leachate treatment plant, will have to meet the non-wastewater standard before disposal in a landfill. The standard for non-wastewater includes 205 45th Purdue Industrial Waste Conference Proceedings, © 1991 Lewis Publishers, Inc., Chelsea, Michigan 48118. Printed in U.S.A. 599
Object Description
Purdue Identification Number | ETRIWC199070 |
Title | Evaluation of a full-scale physico-chemical treatment plant for removal of BDAT constituents from hazardous waste landfill leachate |
Author |
Liu, Bill Y. M. Li, Alan Y. Henry, Michael P. Kruckel, Bruce |
Date of Original | 1990 |
Conference Title | Proceedings of the 45th Industrial Waste Conference |
Conference Front Matter (copy and paste) | http://e-archives.lib.purdue.edu/u?/engext,41605 |
Extent of Original | p. 599-608 |
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 |
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Color Depth | 8 bit |
Description
Title | page 599 |
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 Eight LANDFILLS-B. LEACHATES 70 EVALUATION OF A FULL-SCALE PHYSICO-CHEMICAL TREATMENT PLANT FOR REMOVAL OF BDAT CONSTITUENTS FROM HAZARDOUS WASTE LANDFILL LEACHATE Bill Y. M. Liu, Project Engineer Alan Li, Project Manager Michael P. Henry, Project Manager Chemical Waste Management, Inc. Research and Development Geneva, Illinois 60134 Bruce Kruckel, Operational Manager Chemical Waste Management, Inc. Model City, New York 14107 INTRODUCTION Leachate, generated by water percolating through landfills, can be classified into the two broad categories: non-hazardous and hazardous leachates. Basically, hazardous leachate is generated from hazardous waste or co-disposal landfills, whereas non-hazardous leachate is generated from hazardous waste or co-disposal landfills, whereas non-hazardous leachate is defined as leachate from non- hazardous solid waste landfills. Because of the high concentrations of contaminants in leachate, leachate is generally treated before it can be discharged or disposed of.1 Both types of leachate can be treated with conventional wastewater treatment technologies, such as biological treatment for organic removal, metal precipitation for metal removal and granular activated carbon (GAC) adsorption for effluent polishing.1 The effluent from these leachate treatment plants usually discharges into Publically Owned Treatment Works (POTWs) or to surface waters under state or federal National Pollution Discharge Elimination System (NPDES) permits. The treatment residues are then disposed of in a hazardous landfill for hazardous treatment residues and a solid waste landfill for non-hazardous residues. However, the treatment practice for hazardous waste leachate will be significantly impacted and might have to change when the EPA promulgates the Third-Third landban regulation regarding multi-source leachate on May 8, 1990. The EPA has set on overall schedule for the land disposal program, which requires all land disposal restriction regulations to be in place by May 8, 1990.2 The EPA divided listed hazardous wastes into three groups (the "Third"), to be regulated in successive stages over a period of 66 months. The multi- source hazardous leachates, regulated by the Third Third, will have to meet the treatment standards for wastewaters and non-wastewaters before land disposal.3 The EPA developed the standards representing the best demonstrated available technology (BDAT). The BDAT constituents, totalling 231 compounds, include volatile organics (63 constituents) and semi-volatile organics (107 constituents), metals (16 constituents), inorganics other than metals (3 constituents), organochlorine pesticides (20 constituents), phenoxyacetic acid herbicides (3 constituents), organophosphorus insecticides (5 constituents), polychlorinated biphenyls (7 constituents) and dioxins and furans (7 constituents). In the proposed rule for the Third Third landban2, leachate has to meet the wastewater standard, consisting of 228 BDAT compounds, before land disposal in the surface impoundment. Treatment residues, such as metal and biological sludges from the leachate treatment plant, will have to meet the non-wastewater standard before disposal in a landfill. The standard for non-wastewater includes 205 45th Purdue Industrial Waste Conference Proceedings, © 1991 Lewis Publishers, Inc., Chelsea, Michigan 48118. Printed in U.S.A. 599 |
Resolution | 300 ppi |
Color Depth | 8 bit |
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