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High-Solids, Biological Aeration of Unneutralized, Unsettled Tannery Wastes DWIGHT B. EMERSON Research Assistant NELSON L. NEMEROW, Professor Department of Civil Engineering Syracuse University Syracuse, New York INTRODUCTION In 195 2, there were 443 reported tanneries in the United States (1). About 60 per cent of these tanneries were located in the northeast. In 1965, the number has been reported to have dwindled to about 200 relatively large plants (1). In 1952, Harnley indicated that about 20 bil gal of waste were generated yearly by the tanning industry in the United States. In 1963, an estimated 16 bil gal were discharged by the industry (1). There appears to have been a trend toward centralization during this period in Chicago, Milwaukee, and the northeast. In 1967, the tanneries of the United States represented a five billion dollar industry and employed approximately 40,000 workers. The estimated per capita expenditure for leather goods that year was about 29 dollars. Hide and skin exports are reported to have increased to 82 million dollars during the period between 1963- 64 (1). A current trend has been to export cattle hides to countries which can produce leather at a lower cost. Leather substitutes and imported leather goods have cut into the United States' leather tanner's market. The ability of the United States tanners to meet this competition will depend primarily on economic factors, one of which is the cost of waste water treatment. An estimated 34 million cattle are butchered annually in the United States. About 25 million of these skins are tanned in the United States, with the remainder being exported to foreign markets (1). About 85 per cent of all leather used in the United States is made into shoes, 80 per cent of which is chrome tanned upper leather (1). THE TANNING PROCESS The chrome tanning of cattle hides may be broken down into several process steps, which are indicated in Figure 1. Each step performs an important function in the tanning process and produces a liquid waste. Curing of the hide is usually the first process step performed after the hide is removed from the animal. Bacteria are often abundant on the skin and upon the death of the animal, proteolytic bacteria attack the skin and destroy its potential value as leather. A common method of reducing bacterial action is by dehydrating the skin by treating with salt. -867-
Object Description
Purdue Identification Number | ETRIWC1969056 |
Title | High solids, biological aeration of unneutralized, unsettled tannery wastes |
Author |
Emerson, Dwight B. Nemerow, Nelson Leonard |
Date of Original | 1969 |
Conference Title | Proceedings of the 24th Industrial Waste Conference |
Conference Front Matter (copy and paste) | http://earchives.lib.purdue.edu/u?/engext,16392 |
Extent of Original | p. 867-879 |
Series | Engineering extension series no. 135 |
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 | 2009-05-21 |
Capture Device | Fujitsu fi-5650C |
Capture Details | ScandAll 21 |
Resolution | 300 ppi |
Color Depth | 8 bit |
Description
Title | page 867 |
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 | High-Solids, Biological Aeration of Unneutralized, Unsettled Tannery Wastes DWIGHT B. EMERSON Research Assistant NELSON L. NEMEROW, Professor Department of Civil Engineering Syracuse University Syracuse, New York INTRODUCTION In 195 2, there were 443 reported tanneries in the United States (1). About 60 per cent of these tanneries were located in the northeast. In 1965, the number has been reported to have dwindled to about 200 relatively large plants (1). In 1952, Harnley indicated that about 20 bil gal of waste were generated yearly by the tanning industry in the United States. In 1963, an estimated 16 bil gal were discharged by the industry (1). There appears to have been a trend toward centralization during this period in Chicago, Milwaukee, and the northeast. In 1967, the tanneries of the United States represented a five billion dollar industry and employed approximately 40,000 workers. The estimated per capita expenditure for leather goods that year was about 29 dollars. Hide and skin exports are reported to have increased to 82 million dollars during the period between 1963- 64 (1). A current trend has been to export cattle hides to countries which can produce leather at a lower cost. Leather substitutes and imported leather goods have cut into the United States' leather tanner's market. The ability of the United States tanners to meet this competition will depend primarily on economic factors, one of which is the cost of waste water treatment. An estimated 34 million cattle are butchered annually in the United States. About 25 million of these skins are tanned in the United States, with the remainder being exported to foreign markets (1). About 85 per cent of all leather used in the United States is made into shoes, 80 per cent of which is chrome tanned upper leather (1). THE TANNING PROCESS The chrome tanning of cattle hides may be broken down into several process steps, which are indicated in Figure 1. Each step performs an important function in the tanning process and produces a liquid waste. Curing of the hide is usually the first process step performed after the hide is removed from the animal. Bacteria are often abundant on the skin and upon the death of the animal, proteolytic bacteria attack the skin and destroy its potential value as leather. A common method of reducing bacterial action is by dehydrating the skin by treating with salt. -867- |
Resolution | 300 ppi |
Color Depth | 8 bit |
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