Waste incineration method

Abstract

A basket for incinerating waste inside an incinerator for a duration longer than fifteen minutes with no need for waste to be molten earlier, particularly when waste is introduced inside the incinerator. The basket includes mainly of a glass fiber envelope: it is preferably stiffened by a lightweight metal structure located inside or outside the envelope or built into it. A gripping handle is installed on top of the assembly that is stiffened at the top by a metal tube to which a lightweight metal structure is fixed and by a base formed from a drip pan fixed to the base of the lightweight metal structure.

Claims

1. Method for incinerating waste in a waste vitrification incinerator, the method including steps of: placing the waste to be incinerated in a support basket of waste to be inserted into and incinerated in the incinerator, the support basket comprising an envelope made of at least a coating of glass fibre stiffened by a lightweight metal structure, the envelope being woven with a mesh size defining a porosity adapted for: maintaining the waste in the basket during introducing the basket into the incinerator, controlling thermochemically the speed of the pyrolysis of the waste, particularly the progressive rising of the temperature of the waste until the entire incineration of the waste in the basket, and filtering the pyrolysis gas, wherein the support basket and the waste are disposed in a gas atmosphere, above a molten glass bath, and performing a pyrolysis and a combustion, confining toxic particles in the basket for a duration longer than a pyrolysis and combustion of waste without a basket so that complete combustion can be achieved.

2. Method according to claim 1, wherein after complete combustion of the waste, the glass fibre basket containing waste combustion residues is dissolved in the molten glass bath.

Description

LIST OF FIGURES

(1) The invention and its technical characteristics will be better understood after reading the description that is accompanied by several figures representing the following respectively:

(2) FIG. 1, a sectional view of a first embodiment of the basket according to the invention;

(3) FIG. 2, a sectional view of a second embodiment of the basket according to the invention;

(4) FIG. 3, a sectional view of a third embodiment of the basket according to the invention;

(5) FIG. 4, a graph illustrating operation of the method according to the invention; and

(6) FIG. 5, a sectional view of a fourth embodiment of the basket according to the invention.

DETAILED DESCRIPTION OF SEVERAL EMBODIMENTS OF THE INVENTION

(7) The concept according to the invention consists of putting the waste packet to be incinerated into a basket composed largely of unwoven or more or less tightly woven glass fibre. The tightness of the glass fibre(s) makes it possible to manage contact between the contained waste and the hot and oxidising atmosphere inside the incinerator, weaving allowing variable thermal and gas exchanges. The basket is preferably stiffened by a lightweight metal structure.

(8) The use of non-combustible glass fibre with a high melting point allows mechanical transfer of the waste bag from the waste inlet lock to the incineration zone, thus preventing any loss of content of the basket during the transfer.

(9) The principle of using the glass fibre for making the basket is that this glass fibre surrounds the waste basket and thus delays its temperature rise. This prevents excessively fast fusion and/or pyrolysis of the organic waste, particularly during transfer from the inlet lock to the incinerator.

(10) In the furnace (or incinerator), the content of the basket, namely the waste, is heated progressively. This temperature rise leads to pyrolysis of organic materials. Pyrolysis gases escape from the basket to burn in the oxidising atmosphere of the furnace. The choice of the glass fibre envelope that partly forms the basket, and its porosity and the tightness of its weaving can slow heat transfers towards the inside of the basket and gas transfers towards the outside. Thus, the size of the woven mesh is adapted to the type of waste. Therefore this can manage the pyrolysis and combustion rate of the waste contained in the basket. This thus minimises the size of gas gusts generated by sequential inlet of complete waste bags into the incinerator.

(11) Furthermore, the porosity of the glass fibre envelope forming the basket with its more or less tight weaving, also helps to minimise losses of ash and non-volatile toxic elements contained in the gases inside the incinerator. Therefore this porosity can be adapted to the size of the solid toxic particles which must not be entrained in the gases.

(12) With reference to FIG. 1, according to a first embodiment of the basket according to the invention, the envelope 10 composed of glass fibre is located inside the lightweight metal structure 12. This lightweight metal structure is welded to the bottom of the basket that is advantageously composed of a drip pan 18 located below the envelope 10. The mesh advantageously forming the lightweight metal structure 12 is preferably cylindrical and is welded at the top to a metal tube 16 that will stiffen it. The function of the drip pan 18 forming the bottom of the basket is to collect any metal drops or other molten material drops if the waste contains this type of material with a low melting point that could, for example, melt prematurely in the inlet lock (in another type of embodiment the drip pan could be made of very tightly woven glass fibres that are made practically leak tight to liquids). In this embodiment, the entire basket is completed by a gripping handle 14 fixed on and above the metal tube 16.

(13) In one example of this embodiment, the inside diameter of the envelope 10 made of glass fibre is equal to about 500 mm and its height is about 750 mm. In this case, the weight of the envelope is of the order of 1 kg for glass fibre woven at 45° with a mass per unit area equal to 600 g/m.sup.2. The drip pan 18 is preferably made of stainless steel and its thickness is of the order of one millimeter. The mesh forming the lightweight metal structure 12 is a stainless steel wire with a diameter of between 2 and 5 mm.

(14) In this first embodiment, the large outside diameters for manipulations of the basket in the lock and in the incineration zone are fixed by the lightweight metal structure 12 used.

(15) With reference to FIG. 2, the second embodiment according to the disclosed invention uses a glass fibre envelope 20 located outside the lightweight metal structure 22. This lightweight metal structure is also composed of a cylindrical mesh welded at the top to a metal tube 26 above which there is a gripping handle 24. The base of the assembly is preferably composed of a drip pan 28 that can be installed inside the glass fibre envelope 20. In this embodiment, this makes it easier to fill the basket with waste.

(16) With reference to FIG. 5, the mesh wires forming the lightweight metal structure 52 are integrated into the weaving of the glass fibre forming the envelope 50. The drip pan 58 can then be installed inside or outside the glass fibre envelope 50. In the embodiment shown, the glass fibres forming the envelope pass alternately on opposite sides of the mesh wires forming the lightweight metal structure 52. This version is difficult to make, but it combines the advantages of the two previously disclosed embodiments.

(17) With reference to FIG. 3, according to a third embodiment, the basket comprises two glass fibre layers 30A and 30B placed one inside the other. The function of the outer layer 30A is to filter pyrolysis gases to remove dust. The function of the inner layer 30B is to contain waste with appropriate mechanical strength properties. Note that the function or the position of the two layers could also be inverted. These two layers 30A and 30B are preferably separate. The lightweight metal structure 32 is then located between these two layers 30A and 30B. These three elements 30A, 30B and 32 may be attached to each other by stitching with glass fibres or metal wire.

(18) Therefore the incineration method according to the invention uses the basket mentioned above to incinerate waste inside an incinerator for a duration at least fifteen minutes longer than for pyrolysis and combustion of waste without a basket (incineration time increased by a factor of three or even ten depending on the basket). The waste is thus placed above a molten glass bath above which there is a combustion zone in an atmosphere of oxygen diluted in argon and heated by arc plasma transferred between two electrodes.

(19) FIG. 4 shows water, carbon dioxide and carbon monoxide contents in outlet gases from the vitrification incinerator as a function of time. Water is shown in dashed lines, carbon dioxide in thick lines and carbon monoxide in thin lines.

(20) It can be seen that if waste is sent directly to the surface of a molten glass bath, at time denoted 16h45, the duration of pyrolysis and combustion is very short, in other words of the order of 3 minutes and the added oxygen is insufficient to guarantee complete combustion of the gust of pyrolysis gas. There is a remaining content of the order of 3 to 4% of carbon monoxide in the gas at the outlet from the reactor.

(21) If a basket according to the invention is used, particularly together with its glass fibre envelope, waste is kept suspended above a melting glass bath at time marked 15h42. Its combustion time is increased to 17 minutes until time marked 15h59. This can give complete combustion without the presence of carbon monoxide in the reactor outlet gases.

(22) This result is obtained with the glass fibre envelope acting to retard the beginning of combustion 1, and delay pyrolysis/combustion. This results in complete combustion of waste without oversizing the installation, and particularly the supply of oxidising gas and gas treatment. It also very much minimises the presence of combustion gases at the outlet from the installation.