Vertical shaft furnaces

Specialized metallurgical processes – compositions for use therei – Processes – Producing or treating free metal

Reexamination Certificate

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Details

C075S653000, C266S044000, C266S197000, C266S265000, C266S901000

Reexamination Certificate

active

06245124

ABSTRACT:

BACKGROUND OF THE INVENTION
This invention relates to the operation of vertical shaft furnaces so as to melt metal, particularly to copper shaft furnaces.
Copper shaft furnaces are used in foundries to melt scrap copper for re-use. Such furnaces are usually in the form of an upright cylinder having towards its lower end a water cooled grating. In use, copper scrap is charged into the furnace to rest on the grating. Below the grating fuel is burned, usually with air, in a substoichiometric quantity in order to produce a hot gas mixture which is not oxidizing towards copper (as any of the copper scrap which becomes oxidized during the melting process is effectively lost). The hot gas mixture passes upwardly through the grating and heats the copper scrap by convection sufficiently to melt the copper. Molten copper percolates downwardly through the scrap charge, and passes through the grating to be collected at the bottom of the furnace. From time to time molten metal is tapped off from the bottom of the furnace into a ladle for use in the foundry. Alternatively, the molten metal may be continuously tapped and collected in a suitable receiver.
A common disadvantage of such furnaces is that the waste gas which issues from the surface of the charge is environmentally harmful. This is particularly the case where the copper scrap is contaminated, with organic waxes or lubricants (such as where the contaminated scrap comprises swarf from a machining operation) for example. Smoke and particulates are usually entrained in the waste gas, which may also contain carbon monoxide, unburnt fuel and hydrogen. It is common to treat the waste gas to render it more environmentally acceptable, however although it is relatively straightforward to remove particulates from the waste gas by filtration, treatment of the waste gas to remove or render harmless the carbon monoxide is difficult and expensive, particularly in the presence of unburnt fuel and/or hydrogen which present a risk of explosion.
SUMMARY OF THE INVENTION
Accordingly, the present invention provides a method of operating a copper shaft furnace comprising charging the furnace with contaminated copper scrap to a level at least one furnace diameter below the furnace upper rim, burning at least one stream of fuel with a substoichiometric quantity of air or oxygen-enriched air and thereby forming a hot gas mixture which is substantially non-oxidizing to copper, passing the hot gas mixture upwardly through the scrap charge in the furnace and thereby melting the copper and entraining contaminants in waste gas which pass upwardly from the scrap charge, and introducing a hot oxidizing atmosphere into the shaft furnace at least one furnace diameter above the upper level of the scrap charge to react with substantially all of the waste gas.
The hot oxidizing atmosphere reacts with the waste gas, causing combustion of any unburnt fuel or hydrogen and converts carbon monoxide (CO) to less objectionable carbon dioxide. Surprisingly, it has been found that when treated in this way, typical waste gases contain no visible smoke or fumes, showing that the method of the invention also combusts the entrained organic particulate matter.
Just as it is important that the hot gas mixture is effectively non-oxidizing in order to prevent the oxidation, and thus, loss of copper, so it is important that the hot oxidizing atmosphere is prevented from coming into contact with the top surface of the scrap charge. This is achieved by ensuring that the hot oxidizing atmosphere is introduced into the furnace sufficiently above the scrap charge that all of the oxidant is directed away from the scrap charge by the upward flow of waste gas therefrom. It is also important that the oxidizing atmosphere be hot enough for combustion with the waste gas to be self-sustaining.
To allow the reaction between the waste gas and the hot oxidizing atmosphere to finish before the waste gas leaves the top of the furnace and enters the waste gas treatment system, the hot oxidizing atmosphere is preferably introduced into the shaft furnace at least one furnace diameter below the upper rim of the shaft. While this might be thought disadvantageous in that it prevents charging the furnace to its maximum upper limit, this is surprisingly not the case. It has been found that lowering the level of the top surface of the charge leads to an increase in temperature in the charge, possibly due to the additional heat supplied to the top of the charge by the combustion reaction of the waste gas with the hot oxidizing atmosphere. This temperature increase leads to more rapid melting and hence shorter periods between successive scrap chargings. Accordingly, the present invention can maintain or even improve furnace throughput.
The hot oxidizing atmosphere may be introduced so as to produce at least one substantially axi-symmetric (relative to the vertical axis of the furnace) layer of hot oxidizing atmosphere within the furnace with the layer or each layer being at least one furnace diameter above the upper level of the scrap charge.
As stated above, the layer or each layer is provided at least one furnace diameter below the furnace upper rim. The term “rim” also encompasses the lower edge of a scrap charge door, if one is used in the furnace in question. The hot oxidizing atmosphere is conveniently produced by two or more oxygen/fuel burners operated superstoichiometrically. Altematively, the hot oxidizing atmosphere may be provided by air/fuel burners which are operated with an oxygen lance to give under-flame oxygen enrichment, as is known in the art. This is, however, a less preferable method as typically it would tend to increase the NO
x
level in the waste gas. Burners are preferably angled downwardly, towards the scrap charge, at about 15° to the vertical. Enrichment can be used to draw the flame down towards the scrap charge.
If oxy/fuel burners are used, these are preferably operated superstoichiometrically with at least a 15% excess of oxygen over that required for complete combustion of the fluid, and more preferably with a 50 to 70% excess. However, in practice this will be determined by the levels of smoke and CO being emitted. Suitable burners are described in U.S. Pat. No. 5,882,184 and, in the event unacceptably high NO
x
levels are present, U.S. Pat. No. 5,994,507, which are hereby incorporated by reference. Further excess oxygen can be introduced using the air port of an air/oxy/fuel burner in order to raise the oxygen level in the furnace, where appropriate.


REFERENCES:
patent: 3199977 (1965-08-01), Phillips et al.
patent: 5149363 (1992-09-01), Contrucci et al.
patent: 5518524 (1996-05-01), Wilson et al.
patent: 5611289 (1997-03-01), Brookes
patent: 3009934 A1 (1981-09-01), None
patent: 4115269 (1991-11-01), None
patent: 2 248 325 (1975-05-01), None
Derwent Abstract of CA-1333973, Issued Jun. 15, 1988 XP-002146523.*
Claus Meyer-Wulf, “Verminderung der Emissionen Traditioneller Kupfer-Schachtöfen durch Sauerstoffeindüsung und andere Massnahmen im Bereich der Gicht” Erzmetall 47(1994) Nov. pp 658-662.

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