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11 IN SITU VITRIFICATION APPLICATIONS TO HAZARDOUS WASTES Stephen C. Liikala, Chemical Engineer MAECORP INCORPORATED Homewood, IL 60430 INTRODUCTION In Situ Vitrification (ISV) utilizes electrical energy to melt contaminated soils into a durable glass form. An electric current is passed between electrodes placed in the soil which creates temperatures high enough to melt the soil and produce a molten mass. The vitreous zone pyrolyzes organic compounds and encapsulates the inorganic compounds. Process gases emitted from the melt are collected and routed through a process gas treatment system. When power to the electrodes is shut off, the molten mass cools into a glass form that resembles natural obsidian. Subsidence of the vitrification zone, due to soil densification, is then covered with clean backfill. PROCESS DESCRIPTION In Situ Vitrification (ISV) is a hazardous waste remediation process which converts contaminated soils into a durable glass form through the use of electricity. An array of four molybdenum electrodes are inserted into the contaminated soil and an electrical current is passed between the electrodes. To establish a start up conductive path between the electrodes, a small trench (approximately 2 inches in diameter) is formed in a diagonal "x pattern" and the trench is packed with large flaked graphite powder and glass frit. Power to the electrodes is started and the graphite begins to heat up the adjacent soils creating a conductive molten zone. Convective currents within the melt distribute the wastes evenly throughout the molten mass,1 and the melt depth is determined by the length of the electrodes and their separation. The process gases emitted from the melt are collected by covering the melt with an "off gas hood" and routed through a vapor treatment system. The ISV system currently being designed for applications to hazardous waste sites is mounted on two semi trailers for easy transport from site to site. The first trailer (the support trailer) houses a 3750 kVA transformer and an ethylene glycol cooling system. The second trailer, or the off gas trailer, is divided with half of the trailer housing the process gas treatment equipment and the other half containing the distributed process control system. Other major components of the ISV system include the off gas hood, and portable diesel generators, if desired, for operation in remote areas. The off gas treatment system cools, scrubs, and filters the gaseous effluents from the hood.2 The gases are first passed through a quencher for cooling and removing particulates. A tandem nozzle scrubber then removes remaining particulates and condenses semi volatile components. A vane separator, or mist eliminator, then removes the remaining liquid droplets within the gas. A caustic scrub solution is used to quench and scrub the gases and is contained in a scrub solution tank. The scrub solution is recirculated through a single pass heat exchanger to remove the heat. The scrubbed gases are then heated to remove all moisture prior to filtering. Filtering is accomplished by passing the gases through high efficiency particulate (HEPA) filters, followed by a final polish with vapor phase activated carbon. The gases are drawn through the system by a blower assembly and exhausted out of the top of the off gas trailer. The melt is monitored and controlled by a distributed process control system. The electrical system consists of a 3750 kVA transformer with a scott-tee transformer used to convert three phase line power into two phase power for delivery to the electrodes. The transformer is equipped with multiple voltage taps for maximum power efficiency. Voltages are achievable from 4160 to 310 V at an amperage from 450 to 4000 A per electrode pair.2 As the melt grows in size, the resistance between the electrodes decreases according to the following power equation:' P = I2 x R (1) 43rd Purdue Industrial Waste Conference Proceedings, © 1989 Lewis Publishers, Inc., Chelsea, Michigan 48118. Primed in U.S.A. 83
Object Description
Purdue Identification Number | ETRIWC198811 |
Title | In situ vitrification applications to hazardous wastes |
Author | Liikala, Stephen C. |
Date of Original | 1988 |
Conference Title | Proceedings of the 43rd Industrial Waste Conference |
Conference Front Matter (copy and paste) | http://e-archives.lib.purdue.edu/u?/engext,39828 |
Extent of Original | p. 83-86 |
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 | 2009-08-12 |
Capture Device | Fujitsu fi-5650C |
Capture Details | ScandAll 21 |
Resolution | 300 ppi |
Color Depth | 8 bit |
Description
Title | page 83 |
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 | 11 IN SITU VITRIFICATION APPLICATIONS TO HAZARDOUS WASTES Stephen C. Liikala, Chemical Engineer MAECORP INCORPORATED Homewood, IL 60430 INTRODUCTION In Situ Vitrification (ISV) utilizes electrical energy to melt contaminated soils into a durable glass form. An electric current is passed between electrodes placed in the soil which creates temperatures high enough to melt the soil and produce a molten mass. The vitreous zone pyrolyzes organic compounds and encapsulates the inorganic compounds. Process gases emitted from the melt are collected and routed through a process gas treatment system. When power to the electrodes is shut off, the molten mass cools into a glass form that resembles natural obsidian. Subsidence of the vitrification zone, due to soil densification, is then covered with clean backfill. PROCESS DESCRIPTION In Situ Vitrification (ISV) is a hazardous waste remediation process which converts contaminated soils into a durable glass form through the use of electricity. An array of four molybdenum electrodes are inserted into the contaminated soil and an electrical current is passed between the electrodes. To establish a start up conductive path between the electrodes, a small trench (approximately 2 inches in diameter) is formed in a diagonal "x pattern" and the trench is packed with large flaked graphite powder and glass frit. Power to the electrodes is started and the graphite begins to heat up the adjacent soils creating a conductive molten zone. Convective currents within the melt distribute the wastes evenly throughout the molten mass,1 and the melt depth is determined by the length of the electrodes and their separation. The process gases emitted from the melt are collected by covering the melt with an "off gas hood" and routed through a vapor treatment system. The ISV system currently being designed for applications to hazardous waste sites is mounted on two semi trailers for easy transport from site to site. The first trailer (the support trailer) houses a 3750 kVA transformer and an ethylene glycol cooling system. The second trailer, or the off gas trailer, is divided with half of the trailer housing the process gas treatment equipment and the other half containing the distributed process control system. Other major components of the ISV system include the off gas hood, and portable diesel generators, if desired, for operation in remote areas. The off gas treatment system cools, scrubs, and filters the gaseous effluents from the hood.2 The gases are first passed through a quencher for cooling and removing particulates. A tandem nozzle scrubber then removes remaining particulates and condenses semi volatile components. A vane separator, or mist eliminator, then removes the remaining liquid droplets within the gas. A caustic scrub solution is used to quench and scrub the gases and is contained in a scrub solution tank. The scrub solution is recirculated through a single pass heat exchanger to remove the heat. The scrubbed gases are then heated to remove all moisture prior to filtering. Filtering is accomplished by passing the gases through high efficiency particulate (HEPA) filters, followed by a final polish with vapor phase activated carbon. The gases are drawn through the system by a blower assembly and exhausted out of the top of the off gas trailer. The melt is monitored and controlled by a distributed process control system. The electrical system consists of a 3750 kVA transformer with a scott-tee transformer used to convert three phase line power into two phase power for delivery to the electrodes. The transformer is equipped with multiple voltage taps for maximum power efficiency. Voltages are achievable from 4160 to 310 V at an amperage from 450 to 4000 A per electrode pair.2 As the melt grows in size, the resistance between the electrodes decreases according to the following power equation:' P = I2 x R (1) 43rd Purdue Industrial Waste Conference Proceedings, © 1989 Lewis Publishers, Inc., Chelsea, Michigan 48118. Primed in U.S.A. 83 |
Resolution | 300 ppi |
Color Depth | 8 bit |
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