The invention relates to a process for recycling the metals contained in the electronic boards of waste electrical and electronic equipment (W3E or WEEE).
An electronic board is a printed circuit onto which various types of electronic components are welded. These boards are found in a lot of electrical and electronic equipment (EEE) such as cell phones, printers or else computers. They are generally composed of 35% of generic and precious metals, 35% of glass fibers (or siliceous fibers) constituting the reinforcement of the board, and of 30% of organic materials such as plastics and resins. In terms of precious metals it is possible therein to find gold in processors and on the connections, palladium in multilayer ceramic capacitors (MLCC) and some transistors, tantalum in certain capacitors and silver in integrated circuits.
Table 1 shows examples of the compositions of cell phones, personal computers (PCs) and their impact on the annual metal demand (UNEP 2013).
The global sale volumes of these devices suggest that they contain large amounts of metals.
Several metal recycling processes are already known (cf. Delfini et al. 2011. Journal of Environmental Protection. 2, 675-682). Thus, electronic boards derived for the most part from production scrap are treated by hydrometallurgy in order to recycle the gold that they contain. Other electronic boards are treated by pyrolysis in order to eliminate the resin and concentrate the precious metals. The precious metals are then recovered by pyrometallurgical or hydrometallurgical routes. These processes are harmful to the environment since they require the use of organic solvents. Specifically, as regards the pyrolysis treatment, the metals obtained from this process are sooted up and must then be subjected to a hydrometallurgical treatment. Furthermore, the pyrometallurgical treatment requires prior grinding to a fine particle size which is associated with a high energy consumption. This fine grinding is responsible for most of the losses of metals to dust.
Supercritical water may be used alone or in combination with an oxygen-generating species (of hydrogen peroxide type) in order to oxidize the organic material. A fluid is said to be supercritical when it is placed under temperature and pressure conditions beyond its critical point. The temperature and pressure pair of the critical point of water is Tc=374° C., Pc=22.1 MPa. Under these supercritical conditions, water has solvating properties similar to those of a hexane-type organic solvent.
In the case of an H2O/O2 mixture, the degree of decomposition of the organic molecules may reach 99.99%, with, as gaseous compounds emitted, CO2, N2, excess O2, or even CO in trace amounts if the temperature of the reaction is below 500° C. Thus, the supercritical water oxidation technique may generate, under appropriate conditions, effluents that are directly compatible with the environment.
At the same time, and due to the decrease in the dielectric constant and in the ionic dissociation constant of water in these temperature and pressure ranges, the solubility of the mineral salts decreases greatly.
The organic material oxidation reaction is exothermic, which makes it possible, for contents of organic material in the effluent of greater than approximately 4 wt %, to have a process that is self-sufficient in terms of heating energy (cf. Moussière et al. 2007. The Journal of Supercritical Fluids. 43, 324-332).
A metal recycling process is known from Xiu et al. (2013. Waste Management. 33, 1251-1257) that comprises a step of treating under supercritical conditions. The solvent used is water, with or without oxidizing agent (hydrogen peroxide). In this process, the treatment under supercritical conditions is carried out on electronic boards previously ground to a particle size of less than 3 mm. The step of treating under supercritical conditions is carried out in a reducing medium or in an oxidizing medium. During this step, the organic material is destroyed and eliminated in the effluents. This step is then followed by a separation of the siliceous fibers by hydrochloric acid.
This prior art process therefore requires a prior step of grinding to a very fine particle size which, like the pyrometallurgical treatment, generates dust and leads to losses of metals. The fine grinding step is also associated with a high energy consumption.
The objective of the invention is to propose an alternative process that has none or only some of these drawbacks and that enables an improved recycling of metals present in electronic boards.
For this purpose, one subject of the invention is a process for separating metals from electronic boards, characterized in that it comprises:
In the process of the invention, the fragmentation of the starting materials, if it is used, is advantageously performed to coarser particle sizes than the conventional treatments. Unlike the teaching of the prior art, this fragmentation of coarser size does not reduce the yield, but increases it by preventing or substantially minimizing the losses due to the creation of dust resulting from the grinding.
The objective of the fragmentation is in particular to obtain fragments of small enough size so that they can be introduced into the reactor in which the treatment under supercritical conditions takes place. Thus, for a treatment in a reactor having a relatively large capacity, it may not be necessary to grind the electronic boards. The process may therefore be used on complete boards. This particular embodiment is therefore advantageous since it does not require a shredding device. It is also faster. In this embodiment, the risk of loss of materials is also reduced because the process does not include, in contrast to the other embodiments, a step of transferring the materials. However, for reactors of smaller capacity, fragmentation may prove necessary.
A “coarse” fragmentation may also be advantageous for enabling easy transport, avoiding the loss of metals in the dust generated and/or for increasing the exchange area between the water and the material and thus accelerating the degradation kinetics, or optimizing the material surface area treated. Thus, the average particle size of the fragments obtained at the end of a fragmentation step may range from 0.5 to 15 cm, preferably from 0.8 to 10 cm and more preferentially still from 1 to 5 cm.
The expression “average particle size” is understood to mean the particle size, that is to say the measurement of the largest dimension represented by at least 60%, preferably at least 75%, more preferably still 90% of the fragments.
These values are determined by screening through screens with meshes suitable for the particle sizes to be measured.
The fragmentation is carried out by shredding or by grinding, for example using a knife mill.
Advantageously, the grinder is equipped with a screen for carrying out the grading of the fragments resulting from the grinding.
In step a) of treating under supercritical conditions, that is to say under conditions where the temperature is above 374° C. while the pressure is greater than 22.1 MPa, the organic material is destroyed and eliminated in the effluents. The resin from the electronic boards is attacked, which releases the siliceous fibers, and also the metals. The products obtained at the end of this step predominantly consist of the metals initially present in the boards. Conversely, the resin forming the material, and composed of plastics and fibers, is largely eliminated by the attack under supercritical conditions. However, fibers and resin may remain attached to the solid portion of the electronic boards. This step of the process generates very few losses of metals. Indeed, the liquid phase contains very few metallic elements and almost all of the metals are recovered in the solid phase of the supercritical water treatment.
Advantageously, the temperature in the medium ranges from 374° C. to 600° C. for a pressure of 22.1 MPa to 30 MPa. Preferentially, the temperature is above 500° C. and preferentially equal to 600±20° C. Indeed, under temperature conditions below 500° C., there may be a release of traces of carbon monoxide.
Advantageously, the supercritical conditions of the aqueous medium are maintained for a duration greater than or equal to 30 minutes and preferably ranging from 60 minutes to 180 minutes.
Optionally, the medium in which the treatment under supercritical conditions is carried out contains oxygen (for example air) or one or more oxygen-generating species, and in particular hydrogen peroxide. The addition of an oxidant improves the reaction. Furthermore, the addition of a catalyst such as an alkali metal (for example Na2CO3, KHCO3, K2CO3, KOH, and/or NaOH) and/or activated carbon may also improve the reaction.
Optionally, the treatment is carried out in an autoclave and the supercritical conditions are achieved by increasing the temperature, and preferably exclusively by increasing the temperature.
Advantageously, the process according to the invention comprises a step of recycling the aqueous medium used. The liquid resulting from the reaction under supercritical conditions between the electronic boards and the supercritical fluid used may comprise an oily phase. The various phases of the reaction medium are separated. The oily phase, if there is one, can be separated from the aqueous phase by decantation. The aqueous phase may then be purified by addition of sulfate salts and precipitation of its main pollutant that is generally barium. The liquid phase may then be reused as aqueous medium of the process of the invention, optionally with an addition of hydrogen peroxide at the reactor inlet.
The solid phase may be recovered by filtration.
In step b) of crushing the materials in the solid state that are derived from the step of treating under supercritical conditions, the metals are separated from the fibers which had remained bonded thereto. The separation is based on the difference in ductility of the materials present. Specifically, during the crushing, the ductile metal phases are flattened, whereas the siliceous fibers crumble, leading to a modification of the particle size distribution of the sample. The crumbled portions are referred to as “fines”.
Within the meaning of the invention, “crushing” is understood to mean the action of flattening and deforming a body by a strong compression and/or by a violent impact. The crushing is advantageously carried out by moving the object carrying out the compression against the compressed object.
Advantageously, a pressure ranging from 0.08 to 3 kPa per gram of material treated, and preferentially from 0.1 to 2 kPa per gram is exerted.
Metals and fines may easily be separated by a conventional screening step. This separation technique has the advantage of not requiring prior grinding of the boards and of being associated with a good yield. It does not consume reactant and does not generate effluents. Finally, this separation step makes it possible to recover the siliceous fibers.
Advantageously, the crushing takes place in a crusher which is preferentially a drum screen with heavy elements. The heavy elements may be bars or balls. In general there are at least two thereof. They are made of a material to which the metals and the siliceous fibers do not adhere under the hygrometry, temperature and pressure conditions of step b), such as iron. Their weight is between 50 and 500 g per gram of material treated, and preferentially between 100 and 200 g per gram. The size of the meshes of the screen may vary from 1 to 10 mm, preferably from 2 to 5 mm, and more particularly from 1 to 3 mm (for example around 2 mm).
Preferentially, the crusher has a rotational speed of the order of 20 to 100 rpm, preferably 40 to 80 rpm, and more preferentially still from 50 to 70 rpm.
Due to the fact that the crushing takes place in a screen, the grading (that is to say the separation) of the fines and of the metal particles is carried out directly at the outlet of the crusher.
Advantageously, the crushed materials are treated so as to separate the fragments having a size of less than 3 mm, preferentially less than 2 mm and more preferentially still less than 1 mm.
Preferentially, the crushed materials are subjected to a low-intensity magnetic separation, preferentially under a magnetic field ranging from 200 to 600 gauss, preferentially from 300 to 500 gauss and more preferentially still from 375 to 425 gauss.
Another subject of the invention is the use, for the separation of metals from electronic boards, of means for treating in an aqueous medium under supercritical conditions and crushing means, optionally combined with fragmentation means. This use may be carried out under the conditions and with the means described in the present application.
Another subject of the invention is a device that combines the aforementioned means with the conditions described in the application. For example, it may combine a reactor comprising a supercritical medium with a crusher as described in the present application.
The invention will be better understood on reading the following examples, including figures, which are given solely by way of example.
In a first example, laptop computer electronic boards were subjected to a fragmentation using a knife mill equipped with a screen having a 5 cm mesh. This is the (“shredding”) step 1 of the process depicted in
The solid phase was then separated from the liquid phase by filtration on filter paper having a porosity of 2.5 μm, so as to recover all of the solid phase (step 4 of the process depicted in
The solid phase was then passed through a crusher represented in
The metals thus separated from the resin may then be subjected to a low-intensity magnetic separation, under a magnetic field of 400 gauss. The non-ferrous metals, including the precious metals, were thus separated from the scrap iron.
The process described in example 1 was repeated in another example, example 2, but the duration during which the fragments of electronic boards were maintained under supercritical conditions is 2 hours once the pressure and temperature rise is achieved, and not 30 minutes as in example 1. The crushing time was around 1 minute 30 seconds, at the end of which time there were no longer, visually, any particles exiting the screen.
Table 3 indicates the weights of fines and solids obtained respectively in examples 1 and 2.
The appearance of the products before they pass through the bar crusher suggests a better degradation of the resin after two hours of treatment. The smaller percentage of fines for the product obtained after a supercritical oxidation of two hours confirms this observation. Furthermore, the duration of the crushing is also two times shorter.
In a third example, a laptop computer electronic board was subjected, as in examples 1 and 2, to shredding using a knife mill equipped with a screen having a 5 cm mesh. The fragments obtained have a mean size of 5 cm.
30 g of the fragments thus prepared were then introduced into an autoclave having a volume of 300 ml in which they were bought into contact with 30 g of water. The temperature in the autoclave was raised to 600° C. which made it possible to achieve a pressure of 250 bar. These pressure and temperature conditions were achieved in around 30 minutes. The fragments were then maintained under these conditions for 60 minutes, then the autoclave was depressurized.
The solid phase was then separated from the liquid phase by filtration on filter paper having a porosity of 2.5 μm, so as to recover all of the solid phase.
The solid phase was then passed through the crusher described in
The metals thus separated from the resin may be subjected to a low-intensity magnetic separation, under a magnetic field of 400 gauss. The non-ferrous metals, including the precious metals, were thus separated from the scrap iron.
A determination of the local chemical composition was carried out by SEM-EDS in different zones of the board seen in
In the SEM-EDS analysis, a stream of electrons bombards the sample and gives rise to an emission of x-ray photons, the energy spectrum of which characterizes the constituent elements of the material to be analyzed. This spectrum is analyzed by a semiconductor detector which produces voltage peaks proportional to the energy of the photons received (principle of Energy Dispersive Spectroscopy, EDS). The voltage peaks obtained make it possible to quantify the elements emitting at a given energy, expressed in kiloelectron volts (keV). By way of example,
Thus,
A similar characterization to that carried out for the pure solids was performed on the fines recovered after crushing and constituted of the fibers of the reinforcement of the board. The SEM image (
This is confirmed by the results of analysis of the local chemical composition by SEM-EDS (
Table 4 presents the chemical composition data of the liquid phase at the outlet of the step of attack by supercritical water, after the filtration (step 4 of
It appears that the liquid phase contains very few metal elements, in particular very little Ag and Cu. Almost all of the metals are thus recovered in the solid phase of the treatment by supercritical water. The chemical analysis of the fraction of fines obtained after crushing (
Number | Date | Country | Kind |
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1463195 | Dec 2014 | FR | national |
Filing Document | Filing Date | Country | Kind |
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PCT/FR2015/053635 | 12/18/2015 | WO | 00 |