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■ Autoxidation of Wood Distillation Wastes with Oxygen BOYD T. RILEY, JR., Graduate Student JOHN E. KIKER, JR.. Professor CHARLES I. HARDING, Assistant Professor Environmental Engineering Department University of Florida Gainesville, Florida INTRODUCTION The problem of developing technically and economically feasible industrial waste treatment processes challenges the abilities of the environmental engineer. One such process waste is that produced by the wood distillation industry. This industry may be divided into two general classifications as follows: 1) plants utilizing primarily deciduous woods as a raw material, and 2) plants utilizing primarily coniferous woods as a raw material. The kind of plant depends mainly upon the climate at the plant site, which determines the predominant type of tree for the area. Both types of plants produce charcoal but differ somewhat in other products. The research conducted in the preparation of this paper is confined to wastes from the Cabot Carbon Corporation, a plant located in Gainesville, Florida, which processes mainly coniferous woods. The retort operation is a batch process (See Figure 1). The stump wood is placed into rectangular slat-sided iron crates which are mounted on rail cars. A train of several crates is assembled and moved into a retort by a small engine. After it is sealed, the retort is heated by oil burners to about 800 F with the atmosphere inside the retort kept under reducing rather than oxidizing conditions. Essentially all of the liquids present in the woodare driven out as the wood is carbonized. The wood remains in the retort for about eight hrs. The hot retort is opened and the charcoal is moved to cooling chambers which are similar in construction. As soon as oxygen contacts the hot charcoal, it ignites. After the cooling chamber is sealed, the enclosed oxygen is used up and the flames disappear. The charcoal cools for eight hrs after which it is removed from the cooling chambers and stored. After size classification, large pieces are sold as raw material for the production of activated carbon and the small pieces are pulverized, mixed with starch and pressed into briquets. The liquid vapors pass out of the retort and through condensers. The liquids are pumped to unlined settling lagoons where the heavy tars and oils are separated from the aqueous portion of the liquid. The concentrated oils and tars are pumped from the bottom of the settling lagoons to a steam distillation column where they are further fractionated, barreled, and sold. The aqueous portion, known as acid water or pyroligneous acid by the industry, seeps through the sandy walls of the lagoons ana becomes surface drainage. Acid water is either bacteriostatic or toxic. Veijolo and Mustakalio (1) sep- erated wood tars into various gross fractions by solvent extraction, and tested the effects of these fractions on biological systems. They concluded that the resin acid fraction was primarily responsible for the bacteriostasis and that these resin acids were effective in either the acid or salt form. A few of the characteristics of acid water as sampled at Cabot Carbon Corporation are given in Table I, - 926 -
Object Description
Purdue Identification Number | ETRIWC196674 |
Title | Autoxidation of wood distillation wastes with oxygen |
Author |
Riley, Boyd T. Kiker, John E. Harding, Charles I. |
Date of Original | 1966 |
Conference Title | Proceedings of the 21st Industrial Waste Conference |
Conference Front Matter (copy and paste) | http://earchives.lib.purdue.edu/u?/engext,12965 |
Extent of Original | p. 926-942 |
Series |
Engineering extension series no. 121 Engineering bulletin v. 50, no. 2 |
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 | 2009-05-20 |
Capture Device | Fujitsu fi-5650C |
Capture Details | ScandAll 21 |
Resolution | 300 ppi |
Color Depth | 8 bit |
Description
Title | page 926 |
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 |
Capture Device | Fujitsu fi-5650C |
Capture Details | ScandAll 21 |
Transcript | ■ Autoxidation of Wood Distillation Wastes with Oxygen BOYD T. RILEY, JR., Graduate Student JOHN E. KIKER, JR.. Professor CHARLES I. HARDING, Assistant Professor Environmental Engineering Department University of Florida Gainesville, Florida INTRODUCTION The problem of developing technically and economically feasible industrial waste treatment processes challenges the abilities of the environmental engineer. One such process waste is that produced by the wood distillation industry. This industry may be divided into two general classifications as follows: 1) plants utilizing primarily deciduous woods as a raw material, and 2) plants utilizing primarily coniferous woods as a raw material. The kind of plant depends mainly upon the climate at the plant site, which determines the predominant type of tree for the area. Both types of plants produce charcoal but differ somewhat in other products. The research conducted in the preparation of this paper is confined to wastes from the Cabot Carbon Corporation, a plant located in Gainesville, Florida, which processes mainly coniferous woods. The retort operation is a batch process (See Figure 1). The stump wood is placed into rectangular slat-sided iron crates which are mounted on rail cars. A train of several crates is assembled and moved into a retort by a small engine. After it is sealed, the retort is heated by oil burners to about 800 F with the atmosphere inside the retort kept under reducing rather than oxidizing conditions. Essentially all of the liquids present in the woodare driven out as the wood is carbonized. The wood remains in the retort for about eight hrs. The hot retort is opened and the charcoal is moved to cooling chambers which are similar in construction. As soon as oxygen contacts the hot charcoal, it ignites. After the cooling chamber is sealed, the enclosed oxygen is used up and the flames disappear. The charcoal cools for eight hrs after which it is removed from the cooling chambers and stored. After size classification, large pieces are sold as raw material for the production of activated carbon and the small pieces are pulverized, mixed with starch and pressed into briquets. The liquid vapors pass out of the retort and through condensers. The liquids are pumped to unlined settling lagoons where the heavy tars and oils are separated from the aqueous portion of the liquid. The concentrated oils and tars are pumped from the bottom of the settling lagoons to a steam distillation column where they are further fractionated, barreled, and sold. The aqueous portion, known as acid water or pyroligneous acid by the industry, seeps through the sandy walls of the lagoons ana becomes surface drainage. Acid water is either bacteriostatic or toxic. Veijolo and Mustakalio (1) sep- erated wood tars into various gross fractions by solvent extraction, and tested the effects of these fractions on biological systems. They concluded that the resin acid fraction was primarily responsible for the bacteriostasis and that these resin acids were effective in either the acid or salt form. A few of the characteristics of acid water as sampled at Cabot Carbon Corporation are given in Table I, - 926 - |
Resolution | 300 ppi |
Color Depth | 8 bit |
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