METHOD AND EQUIPMENT FOR EXTRACTING CARBON MATERIALS FROM PLASTICS
20200262708 ยท 2020-08-20
Inventors
Cpc classification
B29B17/02
PERFORMING OPERATIONS; TRANSPORTING
B82Y40/00
PERFORMING OPERATIONS; TRANSPORTING
B29B2017/0293
PERFORMING OPERATIONS; TRANSPORTING
B09B3/40
PERFORMING OPERATIONS; TRANSPORTING
B82Y30/00
PERFORMING OPERATIONS; TRANSPORTING
C01B2204/04
CHEMISTRY; METALLURGY
Y02P20/129
GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
F27B9/20
MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
International classification
B01J6/00
PERFORMING OPERATIONS; TRANSPORTING
B09B3/00
PERFORMING OPERATIONS; TRANSPORTING
Abstract
The invention provides a method and equipment for extracting carbon materials from plastics. Particularly, the method produces nanostructured carbon materials by heating of at least one salt (e.g., NaCl) and at least one plastic material (e.g.polyethylene terephthalate) to a temperature greater than the melting point of the said salt, in which molten state of the said salt protects the carbonaceous material from oxidation. Moreover, molten salt promotes the graphitization of carbon materials. The product is in the form of graphenenano-flakes with high conductivity and high surface area. This method provides a simple, economical and efficient approach for producing conductive carbon materials. It also has a significant positive impact on the environment through the transformation of virtually non-degradable plastic wastes into high-value conductive carbon materials.
Claims
1. A method for extracting carbon materials from plastics, wherein nanostructured carbon materials are produced by heating a mixture consisting of at least one plastic and at least one metal halide salt to a heating temperature in the range defined as: the melting point of the saltheating temperaturethe boiling point of the salt+50 C.
2. The method for extracting carbon materials from plastics according to claim 1, wherein the salt is a hydrated metal halide salt.
3. The method for extracting carbon materials from plastics according to claim 1, wherein the heating temperature is above the melting point of the metal halide salts, and less than the boiling temperature of the salts, by which a mixture of nanostructured carbon materials and salts is produced; after the mixture is cooled down, the salts are dissolved by water followed by filtration to retrieve the nanostructured carbon materials and the solution of the water and the salts; the nanostructured carbon materials are collected after drying and the salts are recycled from the solution.
4. The method for extracting carbon materials from plastics according to claim 1, wherein the conductivity of the synthesized nanostructured carbon material is greater than 1000 S m.sup.1 or the value of Raman I.sub.D/I.sub.G is less than 0.5.
5. The method for extracting carbon materials from plastics according to claim 1, wherein the salt is one metal halide salt or a mixture of metal halide salts selected from the group consisting of LiCl, NaCl, KCl, MgCl.sub.2, CaCl.sub.2, NaF and ZnCl.sub.2; the salt can be a hydrated metal halide salt or a mixture of more than one hydrated metal halide salt selected from the group consisting of hydrated forms of LiCl, NaCl, KCl, MgCl.sub.2, CaCl.sub.2, NaF and ZnCl.sub.2.
6. The method for extracting carbon materials from plastics according to claim 1, wherein the plastics include at least one of polyethylene, polypropylene, polyethylene terephthalate, polystyrene, polyvinyl chloride, polylactide, polycarbonate, acrylic acid, nylon and ABS resin or synthetic rubbers.
7. The method for extracting carbon materials from plastics according to claim 1, wherein the heating is carried out in air, inert gas atmosphere, nitrogen atmosphere or vacuum conditions; when the heating atmosphere is an inert gas or nitrogen, the atmosphere contains H.sub.2 above 0.1% volume fraction.
8. The method for extracting carbon materials from plastics according to claim 1, wherein the nanostructured carbon produced has one or more of the following properties: surface area of greater than 500 m.sup.2 g.sup.1; capacitance of greater than 70 F g.sup.1; having a graphitic structure; having a symmetrical Raman 2D band; containing graphene nanolayers with the number of layers of less than 20 layers, with a flake thickness of less than 10 nm.
9. The method for extracting carbon materials from plastics according to claim 1, wherein the metal halide salt is NaCl and the plastic is polyethylene terephthalate (PET), and the heating temperature is above 1100 C.
10. An equipment by which the method for extracting carbon materials from plastics according to claim 1 is implemented, wherein the equipment includes a tunnel furnace with a moving load bracket; the moving load bracket is made of refractory materials or covered with alumina panels fitted on a metallic rail; the upper part of the tunnel furnace is provided with heating elements installed on refractory materials; the heating element can be gas or electricity powdered, providing temperature needed for the reaction; the upper part of the tunnel furnace is provided with a hole connected to a gas extraction system for collecting the gaseous substances released during the reaction process; a refractory container is placed on the moving load bracket, in which the salt and the plastic are loaded, and moves with the moving load bracket during the reaction from one end of the tunnel furnace to the other end, within which the temperature increases and then decreases, and finally the refractory container comes out of the tunnel furnace; a post-treatment and the recycling device is used to treat the reaction products obtained from the refractory container by water after the heating process, by which the salt is dissolved, followed by filtering the suspended nanostructured carbon materials, and dry out the final product; the waste heat from the tunnel furnace is used to evaporate the excess water of the filtration liquid to recover the reactant salt for reuse.
11. The method for extracting carbon materials from plastics according to claim 2, wherein the heating temperature is above the melting point of the metal halide salts, and less than the boiling temperature of the salts, by which a mixture of nanostructured carbon materials and salts is produced; after the mixture is cooled down, the salts are dissolved by water followed by filtration to retrieve the nanostructured carbon materials and the solution of the water and the salts; the nanostructured carbon materials are collected after drying and the salts are recycled from the solution.
12. The method for extracting carbon materials from plastics according to claim 2, wherein the conductivity of the synthesized nanostructured carbon material is greater than 1000 S m.sup.1 or the value of Raman I.sub.D/I.sub.G is less than 0.5.
13. The method for extracting carbon materials from plastics according to claim 2, wherein the salt is one metal halide salt or a mixture of metal halide salts selected from the group consisting of LiCl, NaCl, KCl, MgCl.sub.2, CaCl.sub.2, NaF and ZnCl.sub.2; the salt can be a hydrated metal halide salt or a mixture of more than one hydrated metal halide salt selected from the group consisting of hydrated forms of LiCl, NaCl, KCl, MgCl.sub.2, CaCl.sub.2, NaF and ZnCl.sub.2.
14. The method for extracting carbon materials from plastics according to claim 2, wherein the plastics include at least one of polyethylene, polypropylene, polyethylene terephthalate, polystyrene, polyvinyl chloride, polylactide, polycarbonate, acrylic acid, nylon and ABS resin or synthetic rubbers.
15. The method for extracting carbon materials from plastics according to claim 2, wherein the heating is carried out in air, inert gas atmosphere, nitrogen atmosphere or vacuum conditions; when the heating atmosphere is an inert gas or nitrogen, the atmosphere contains H.sub.2 above 0.1% volume fraction.
16. The method for extracting carbon materials from plastics according to claim 2, wherein the nanostructured carbon produced has one or more of the following properties: surface area of greater than 500 m.sup.2 g.sup.1; capacitance of greater than 70 F g.sup.1; having a graphitic structure; having a symmetrical Raman 2D band; containing graphene nanolayers with the number of layers of less than 20 layers, with a flake thickness of less than 10 nm.
17. The method for extracting carbon materials from plastics according to claim 2, wherein the metal halide salt is NaCl and the plastic is polyethylene terephthalate (PET), and the heating temperature is above 1100 C.
Description
DESCRIPTION OF DRAWINGS
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DETAILED DESCRIPTION
[0039] In order for the invention to be proved, easier to understand and easy to implement by those skilled in the art, the present invention is described by unrestricted examples combined with the corresponding pictures, charts and micrographs, where:
[0040] The preferred reactor, as shown in
[0041] The salt recovered from the mixture of nanostructured carbon and salt is shown as (5). The recovered salt is loaded in the refractory container 6, together with pieces of plastic materials. The salt is preferentially a metal halide or a mixture of metal halides. More preferentially the salt is NaCl or contains NaCl. It is because NaCl is cheap and highly available. Moreover, NaCl has an appropriate melting and boiling point of about 800 and 1400 C., indicating that molten NaCl can protect the carbonaceous materials from severe oxidation at high temperatures greater than 900 C. Also, NaCl has a high solubility in water, and therefore can easily be removed from the system and recovered. The refractory container 6 can be a ceramic crucible such as alumina (Al.sub.2O.sub.3). It can also be a carbon crucible such a graphite crucible, provided if the process is carried out under a protective atmosphere, such as argon or nitrogen, to avoid oxidation of the carbon crucible. To start the heat treatment process, a mixture of plastics and salt is loaded into the crucible. The crucible loaded by a mixture of plastics and salts 7 is then moved into the tunnel furnace by the application of the moving load bracket 1. The temperature inside the tunnel furnace is controlled by the heating elements positioned, preferentially, on the upper part of the tunnel furnace 2. The temperature inside the tunnel furnace is gradually increased as indicated in temperature profile inside the tunnel furnace 4. When the temperature inside the tunnel furnace exceeds the melting point of the plastic materials inside the crucible, the melting of plastic materials 8 occurs. By further moving of the crucible forward in the tunnel furnace, the temperature exceeds the decomposition point of the plastic materials. Consequently, the plastic materials decompose into a gas phase which exits the crucible and solid carbonaceous particles mixed with the solid salt particles 9. The gas phase is evacuated from the tunnel furnace through the hole connected to a gas extraction system 3. Whilst the crucible moves forward, the temperature exceeds the melting point of the salt. By further moving of the crucible in the tunnel furnace, the carbonaceous material undergoes an enhanced graphitization, promoted by the molten salt. At T.sub.max, the graphitization process is accelerated, and the carbonaceous material turn into a nanostructured carbon material dispersed into the molten salt 10. By further moving of the crucible through the tunnel furnace, the temperature decreases to the temperature of T.sub.1 at the exit location. T.sub.1 is less than 500 C., or preferentially less than 400 C., or more preferentially less than 300 C. When the crucible is sufficiently cold 11, its content is exposed to distilled water. It can be done by adding water into the crucible. Consequently, the salt is dissolved into water and a suspension comprising the nanostructured carbon and a liquid phase comprising water and salt is formed. The nanostructured carbon can be extracted by filtration of the suspension through a filter paper. A skilled person knows how to separate the nanostructured carbon materials 12 from the suspension. The liquid phase can then be used to recover the salt. It can be done by the evaporation of water to retrieve the salt. The waste heat generated by the tunnel furnace may be used for the evaporation of water. The salt recovered from the mixture of nanostructured carbon and salt 5 is then transferred to the starting point to be mixed with plastic materials.
[0042] Unless otherwise specified in the examples, the characterization of the materials was performed according to the following methods: electron microscopy evaluations were carried out using a Nova Nano-SEM 450 equipped with energy dispersive x-ray analyser (EDX) and a 200 kV FEI Tecnai F20 field emission gun high resolution TEM (HRTEM). X-ray diffraction (XRD) patterns were recorded on a Philips 1710 X-ray diffractometer (XRD) with CuK.sub. radiation (k=1.54 A with a step size and a dwell time of 0.05 2 and 5 s, respectively. The XRD patterns were then analysed using the X'Pert High Score Plus program. Raman spectroscopy was conducted using a Renishaw 1000 Ramanscope with a HeNe ion laser of a wavelength of 633 nm (red, 1.96 eV). Thermal gravimetry (TG) and differential scanning calorimetry (DSC) were carried out simultaneously using a thermal analyser model SDT-Q600 equipped with alumina crucibles at a heating rate of 40 C. min.sup.1 under a constant air flow rate of 100 ml min.sup.1 through the sample chamber. Brunauer-Emmett-Teller (BET) surface area analysis was performed by recording nitrogen adsorption/desorption isotherms using a static volumetric technique with a Micromeritics TriStar 3000 V6.04 Aanalyser at 196 C. The electrical conductivity measurement was conducted by compressing 0.5 g of the carbon material into an acrylic tube (ID=20.05 mm, H=45.37 mm) using a brass piston (D=20.05 mm, H=85.36 mm) on a copper holder. The carbon powder was compacted using a hydraulic press to build up a pressure on the carbon power up to about 6 MPa. At different pressures, various values of electric currents in the range 0.16-3 A was conducted between the brass piston and the copper holder, and the corresponding potentials were recorded using the four-probe DC method at 20 C. The electrical resistivity of compressed carbon powder was calculated using the equation:
=(SV)/(IH) (1)
[0043] Where is the resistivity ( m), S is the surface area of the acrylic tube's hole (mm.sup.2), V is the potential difference (mV), I is the current (A) and H is the height of the compressed powder (mm) Electrical conductivity was calculated as the reciprocal of electrical resistivity.
[0044] The electrochemical capacitance performance of the carbon product was evaluated using a three-electrode system, in which the working electrode was prepared by mixing the carbon materials with 10% conductive carbon (SP45 with a BET surface area of 45 m.sup.2 g.sup.1) and 10% binder (polytetrafluoroethylene, PTFE). The mixture was loaded on a Ni plate of 1.2 cm in diameter, with a mass loading of 3.3 mg cm.sup.2. The electrolyte was 6 M KOH. A platinum wire and a saturated calomel electrode (Hg/HgCl n saturated KCl) were employed as the counter and the reference electrode, respectively. Cyclic voltammetry (CV), galvanostatic charge-discharge, and electrochemical impedance spectroscopy (EIS) measurements were performed to evaluate the electrochemical performance. The specific capacitance (F g.sup.1) of the supercapacitor fabricated was calculated from the equation:
C.sub.s=(I t)/(m V) (2)
[0045] where I is the discharge current, t is discharge time, in is the mass of active material and V represents the voltage window.
EXAMPLE 1
[0046] Characterization of PET Material
[0047] The XRD diffraction pattern recorded on small pieces of a water bottle is shown in
[0048] The low crystalline PET material was heated in a resistance furnace at 260 C., above the melting point of PET, overnight. After cooling down to the room temperature, the heat treated material obtained, in form of white colour, large and irregular shaped crystalline particles, was subjected to XRD analysis. The diffraction peaks observed in the pattern can be indexed according to the crystalline PET anorthic structure. The most intense (100) reflection peak is observed at 2 theta=26.00 degree. The SEM morphology of the crystalline PET is shown as the inset in
[0049] Gonzalez et al. measured the C:O ratio of virgin and plasma-treated PET to be 3 and 1.7, respectively using XPS analysis (E. Gonzalez II, M. D. Barankin, P. C. Guschl, and R. F. Hicks, Remote atmospheric-pressure plasma activation of the surfaces of polyethylene terephthalate and polyethylene naphthalate, Langmuir 24 (2008) 12636-12643). The higher value of C:O measured on virgin PET was attributed to the presence on surface contaminations. On the other hand, the lower value of C:O in plasma treated PET was explained by the presence of more CO and CO bonds on the surface of PET induced by the plasma treatment. In our case, the lower value of C:O ratio observed based on the EDX analysis can be attributed to the surface electron irradiation of PET occurred during the microscopy. These observations confirm that the crystallisation of PET occurred during its solidification, and that the plastic bottle was made of pure PET. Such material with a high carbon content and no inorganic component is an attracting source for the preparation of solid carbon materials.
[0050] The TGA and DSC thermograms recorded on a small number of PET pieces in the temperature range 25-900 C. can be seen in
[0051] In order to investigate this endothermic peak, small pieces of a PET plastic was heated in a resistance furnace to 650 C. and 850 C., and the black carbon materials obtained were subjected to XRD and SEM analyses.
[0052] It should be mentioned that in the graphite hexagonal structure (JCPDS card No. 13-0148), the (002) reflection appears at the 2=26.6, indicating an interplanar spacing of 3.35 . The reflection peaks (100) and (101) appear at the 2 values of around 42.4 and 44.4, respectively. The large deviation of d.sub.(002) towards a higher value in the turbostratic carbon material produced in comparison to that of graphite indicates the poorly crystalline nature of the material.
[0053] Li et. al identified the turbostratic carbon as a variant of hexagonal graphite, in which the (002) carbon layers may randomly translate to each other and rotate about the normal of the layers.
[0054] In the XRD pattern of PET heat treated at 850 C. (
[0055] The endothermic peak appeared in the DSC curve of
[0056] Further information can be obtained from the SEM morphology of the samples shown in
[0057] It is known that the intensive oxidation of carbon materials in air begins at temperatures over 500 C., depending on the properties of the carbon material including its degree of graphitization, particle size and porosity (V. Zh. Shemet, A. P. Pomytkin and V. S. Neshpor, High temperature oxidation behavior of carbon materials in air, Carbon 31 (1993) 1-6). Thermal oxidation of highly oriented pyrolytic graphite was reported by Hahn to occur at 550-950 C. (J. R. Hahn, H. Kang S. M. Lee, Y. H. Lee, Mechanistic study of defect-induced oxidation of graphite, J. Phys Chem B 103 (1999) 9944-51). At temperatures lower than 875 C., the oxidation process was found to be dominated by the formation of pits at defect sites. At higher temperature, however, the oxidation takes place on both defects and basal planes. It is also known that the rate of oxidation of amorphous carbon is higher than that of graphitic carbon materials. Without being limited by mechanism, the high oxidation resistance of the carbon material produced by the pyrolysis of PET in air can be assigned to its large particle sizes, low porosity and perhaps its low density of surface defects.
EXAMPLE 2
[0058] Heat treatment of PET in NaCl was investigated in this example. A plastic water bottle was cut into small pieces (around 105 mm) using a scissor. 9.83 g of plastic pieces was placed into an alumina crucible with an approximate internal diameter and height of 50 mm and 100 mm, respectively. Then, 50.80 g sodium chloride (NaCl, Aladdin C111533, purity 99.5%) was added to the crucible. The crucible was placed into a resistance furnace and heated in the air atmosphere of the furnace at 20 C. min.sup.1 to 1100 C., and then immediately cooled down with an approximately same heating rate to the room temperature. The black solid mixture of solidified salt and carbon product was placed in sufficient amount of distilled water, in which the salt was dissolved. The carbon product was then recovered from the suspension by vacuum filtration using a filter paper, and left to be dried at 80 C.
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[0060] The Raman spectrum of the carbon product produced by the heat treatment of PET in molten NaCl at 1100 C., shown in the lower panel of
EXAMPLE 3
[0061] In order to investigate the effect of temperature, the mixture of PET-NaCl in the same weight ratio as that of Example 2, and the mixture was heated to 1300 C. by the same heating rate of 20 C. min.sup.1, and then cooled down to the room temperature.
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[0063] TEM microscopy (
[0064] The surface properties of the nanostructured carbon material were studied through the nitrogen adsorption-desorption technique, and the recorded isotherm is presented in
[0065] The results obtained confirm that the heat treatment of PET in molten NaCl leads to the preparation of a carbon nanostructure consisting crystalline graphitic nanosheets and sheet fragments with a thickness of less than 10 nm, and a high surface area.
[0066] It should be mentioned that, together with surface area and crystallinity, the electrical conductivity is one of the most important parameters which determine the performance of carbon materials in practical applications such as supercapacitors, electromagnetic shielding, catalysts, and metal-ion batteries. However, in carbon materials, often the electrical conductivity decreases with the increase in surface area.
EXAMPLE 4
[0067] Nanostructured graphite was produced as explained in Example 3. The electrical conductivity of the carbon material produced was evaluated at various compression pressures using the four probe method.
EXAMPLE 5
[0068] Nanostructures graphite was produced as explained in Example 3. The Electrochemical behavior of the carbon product was evaluated using a three-electrode system with 6 M KOH as the electrolyte. The CV profiles, recorded at various scan rates of 5-200 mV s.sup.1, shown in
[0069]
EXAMPLE 6
[0070] 100 g Sodium fluoride (NaF) was mixed with 20 g PET plastic pieces. The mixture was placed in an alumina crucible and heated to a maximum temperature of 1300 C., and held at this temperature for 1 h in an electric furnace in air. The crucible was then allowed to be cooled down, and the salt was washed off using sufficient amount of water followed by the filtration of the suspension obtained. The black carbon material obtained on the filter paper was dried at 80 C. for 2 h. The Raman spectrum of the carbon material obtained is shown in
EXAMPLE 7
[0071] 50 g MgCl.sub.2.6H.sub.2O was mixed with 10 g PET plastic pieces, and the mixture was placed in an alumina crucible and treated according to the heat treatment and washing process explained in the previous Example 6, with the only difference that the heating process was conducted in a tube furnace under a vacuum of 10.sup.2 mbar. The Raman spectrum of the carbon material obtained is shown in
[0072] The process of producing conductive nanostructured graphitized carbon can be carried out in a continuous manner in the tunnel furnace, as shown in