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The Toxicity of Chromium R. S. INGOLS Research Professor Georgia Institute of Technology Atlanta, Georgia In a study of toxicity there are several problems that one would like to answer. First, how much of the material is required to show a toxic level, or in other words, how much material will be required to bring about a sensible, i.e., major, reduction in the respiration or metabolism of the organism affected ? Second, in order that some means may be found to overcome this toxicity, what is the mechanism of the reaction? And third, what can be understood concerning the chemical reactions and structure of the organism itself from the amount and chemical nature of the toxic agent used under varying conditions? This report brings out how the state of oxidation of chromium (trivalent or hexavalent) affects the organisms and the relationship of the state of oxidation to the environment of the organisms. The variations in the environment include both aerobic and anerobic conditions, as well as several organic matter concentrations. Then, too, the report indicates what practical application these factors have in sewage treatment and in the disposal of sewage or industrial effluents containing some chromium. The report also includes a comment concerning the structure and metabolism of the microorganisms. A study of the literature reporting the effect of chromium upon various sewage-treatment processes, rivers or analytical results indicates confusion about the amount of chromium necessary to give toxicity. One anonymous article (13) indicates that one part per million of hexavalent chromium can not be tolerated in a digestion tank, whereas Barnes and Braidech (3) indicate that 10,000 p.p.m. of chromate give only a 34 percent reduction in the amount of gas generated. This tremendous discrepancy points out a problem; how can two people get such different results? Is the discrepancy the result of the method for determining the amount of chromium that is present, or of the method for evaluating the amount that is added? One can also raise the question of what happens to hexavalent chromium after it has been added to the digestion tank. Does the one report mean that one part per million of chromium remained as chromate after a portion had been reduced, so that the toxicity includes the excess chromate ion 86
Object Description
Purdue Identification Number | ETRIWC195310 |
Title | Toxicity of chromium |
Author | Ingols, R. S. |
Date of Original | 1953 |
Conference Title | Proceedings of the eighth Industrial Waste Conference |
Conference Front Matter (copy and paste) | http://earchives.lib.purdue.edu/cdm4/document.php?CISOROOT=/engext&CISOPTR=3119&REC=9 |
Extent of Original | p. 86-95 |
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 | 2008-09-22 |
Capture Device | Fujitsu fi-5650C |
Capture Details | ScandAll 21 |
Resolution | 300 ppi |
Color Depth | 8 bit |
Description
Title | page 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 |
Capture Device | Fujitsu fi-5650C |
Capture Details | ScandAll 21 |
Transcript | The Toxicity of Chromium R. S. INGOLS Research Professor Georgia Institute of Technology Atlanta, Georgia In a study of toxicity there are several problems that one would like to answer. First, how much of the material is required to show a toxic level, or in other words, how much material will be required to bring about a sensible, i.e., major, reduction in the respiration or metabolism of the organism affected ? Second, in order that some means may be found to overcome this toxicity, what is the mechanism of the reaction? And third, what can be understood concerning the chemical reactions and structure of the organism itself from the amount and chemical nature of the toxic agent used under varying conditions? This report brings out how the state of oxidation of chromium (trivalent or hexavalent) affects the organisms and the relationship of the state of oxidation to the environment of the organisms. The variations in the environment include both aerobic and anerobic conditions, as well as several organic matter concentrations. Then, too, the report indicates what practical application these factors have in sewage treatment and in the disposal of sewage or industrial effluents containing some chromium. The report also includes a comment concerning the structure and metabolism of the microorganisms. A study of the literature reporting the effect of chromium upon various sewage-treatment processes, rivers or analytical results indicates confusion about the amount of chromium necessary to give toxicity. One anonymous article (13) indicates that one part per million of hexavalent chromium can not be tolerated in a digestion tank, whereas Barnes and Braidech (3) indicate that 10,000 p.p.m. of chromate give only a 34 percent reduction in the amount of gas generated. This tremendous discrepancy points out a problem; how can two people get such different results? Is the discrepancy the result of the method for determining the amount of chromium that is present, or of the method for evaluating the amount that is added? One can also raise the question of what happens to hexavalent chromium after it has been added to the digestion tank. Does the one report mean that one part per million of chromium remained as chromate after a portion had been reduced, so that the toxicity includes the excess chromate ion 86 |
Resolution | 300 ppi |
Color Depth | 8 bit |
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