The present disclosure relates to nanocomposite piezoelectric and piezocatalytic materials; the use of these materials in water remediation; and methods of making such materials. Articles formed from or coated with these materials are also considered as part of the present disclosure, as are methods of making such articles.
Piezoelectric materials can produce electric charge when subjected to mechanical stress and vice-versa. Mechanically straining a piezoelectric material induces an electric field throughout the material which generates free charges at its interface with the ambient environment (e.g. air or water). This electric charge can be harnessed as a means of producing electrical power from mechanical motion. For example, this effect has been suggested to be useful in wearable electronics that are powered by movement of the wearer, or harvesting “wasted” energy from sources such as acoustic vibrations.
Piezocatalytic materials are a subclass of piezoelectric materials, where the material composition is such that the free charges generated by mechanical motion in turn generate reactive oxygen species (ROS) including .OH, .O−, .HO2 and H2O2 by local micro-electrolysis in an aqueous environment. A combination of the piezoelectric charge coupled with suitable local microstructure at the surface/interface with the aqueous environment results in this piezocatalytic behaviour. The ROS generated by mechanical actuation of the piezoelectric materials thus can be efficiently used to piezocatalytically oxidize and degrade harmful substances in the aqueous environment.
Bioaccumulation of inorganic and organic contaminants such as toxic dyes, pharmaceuticals, and drugs in wastewater effluents, natural environments and drinking waters has grown at an alarming rate in recent times and presents a huge challenge for water reuse industry. Water pollutants such as common pesticides, herbicides, organic dyes and biological contaminants such as DNA, proteins, lipids, bacteria, virus, spores etc., present a serious and persistent threat to human health. This has prompted the development of some advanced disinfection and water remediation techniques which involve reactive oxygen species (ROS). ROS consisting of a medley of strong oxidizing agents like OH., H., O., O3, H2O2 etc. that can safely and effectively destroy a large number of living and non-living organic contaminants in water. Among the contaminants, organic dyes are particularly challenging to remove or destroy since most dyes used in textile, pharmaceutical, food industries and agriculture are not only toxic to the environment but many are also carcinogenic. Thus, complete breakdown and/or removal of these contaminants in industry effluents and more generally in the aquatic environment is essential both for human health and for the environment. Doing this in a safe and energy-efficient manner is a major scientific challenge.
Current ROS based water treatment technologies such as UV photolysis, radiolysis, ozonation, sonochemistry, electrical discharge technology, electron-beam irradiation and supercritical water oxidation require expensive set up and a continuous energy source in the form of electricity or ultraviolet light. Although, photocatalysis has shown promise, it is limited by agglomeration tendency, post-separation difficulties and low efficiency under solar irradiation.
Piezoelectric ceramics in the form of ZnO and Cu/ZnO nanowires, Pb(Zr0.52Ti0.43)O3 fibers, ZnSnO3 nanowires, single/few-layers MoS2 nanoflowers and nano/micrometer sized BaTiO3, etc. have all been reported to piezocatalytically degrade potentially harmful dyes e.g. Acid Orange 7, Rhodamine B, Methyl Orange, 4-chlorophenol on exposure to ultrasound vibrations. Harnessing the abundant vibrational and otherwise wasted mechanical energy to piezocatalytically treat waste water can boost water purification technology in an energy-efficient manner. However, using free piezoelectric nanoparticles directly in water treatment presents several problems in the form of stability of the nanoparticles, efficacy, accumulation, toxicity, separation and recyclability.
Piezocatalytic activity in MoS2 nanoflowers was first reported by Wu et al. [1], who showed ultrafast degradation of Rhodamine B in water under dark condition. However, for practical application, the process runs the risk of contaminating water with the MoS2 nanoparticles themselves. Furthermore, this process is not suitable for treatment of flowing water due to loss of nanoparticles over time.
Some polymers are known to demonstrate piezoelectric behaviour. For example, polyvinylidene difluoride (PVDF) is known to be piezoelectric under certain conditions. PVDF has four crystalline phases α, β, γ and δ, α being the most stable and non-polar with β and γ being polar phases due to the arrangement of the fluorine groups in the polymer chains. The β form of PVDF demonstrates the largest piezoelectric behaviour. PVDF typically exists in the α form so there is significant interest in piezoelectric research in inducing transition to the piezoelectric β phase. This can be done relatively easily by directed mechanical stretching, by electrospinning, or by application of a strong external aligned magnetic field. The process of transforming the non-piezoelectric material (e.g. a-phase PVDF) to a piezoelectric form (e.g. β-phase) is known as “poling”. Alongside these processes in which energy is added in some format to achieve the poling effect (i.e. inducement of the piezoelectric behaviour), PVDF is also known to undergo “self-poling” under certain specific conditions. For example, some metal-ion doping is known to induce spontaneous formation of the β phase in PVDF [2]. However, this spontaneous self-poling in PVDF occurs only under specific conditions and with specific dopants.
Maity et al. [3] describes a combination of few-layer exfoliated fragments MoS2 with electrospun PVDF to form a composite material in which the addition of few-layer MoS2 improves the piezoelectric behaviour of the PVDF material.
Lin et al. [4] describes combination of MoS2 nanoflowers with poly(dimethyl siloxane) (PDMS) to provide a material having triboelectric (generation of electric charge through relative motion between the material surface and a suitable environment) and piezocatalytic behaviour. This material was shown to degrade dyes in an aqueous environment. However significant degradation of the material was observed with repeated or extended use.
Sahatiya et al. [5] describes piezoelectric and triboelectric nanogenerators comprising a layer of MoS2 nanoflowers formed on a paper substrate with a layer of electrospun PVDF nanofibers on each side of the MoS2 layer. The piezoelectric effect is higher than either of the individual components alone.
There remains a need for materials that address one or more of these challenges. For example there is a desire in the art for improved robust, flexible piezoelectric nanogenerators in general. There also exists a need for effective and robust piezocatalytic materials for use in water remediation.
[1] J. M. Wu et al., Adv. Mater., 28 (2016) pp.3718-3725.
[2] Hoque et al., ACS Appl. Mater. Interfaces (2017), 9, 23048-23059.
[3] K. Maity et al., Energy Technol. 5(2017) pp.234-243.
[4] J. H. Lin et al., Nano Energy 31(2017) pp.575-581.
[5] P. Sahatiya et al., Appl Mater Today, 13(2018), pp.91-99.
The present proposals include a flexible, polymer nanocomposite material as a solution to overcome one or more of these limitations. As such the present proposals relate to piezoelectric and piezocatalytic materials comprising MoS2 nanoflowers embedded throughout a body comprising poly vinylidene difluoride (PVDF). Flexible piezoelectric and piezocatalytic layers, coatings or sheets formed from such materials also form part of the present proposals. Piezoelectric and piezocatalytic devices incorporating these structures are also envisaged herein.
In addition, these proposals relate to use of such materials, layers, coatings or sheets, for piezocatalytic removal of contaminants from an aqueous environment and/or for generation of piezoelectricity. Methods of piezocatalytic removal of contaminants from an aqueous environment, and methods of generating piezoelectricity, by application of mechanical stress to such materials, layers, coatings or sheets are also part of these proposals.
A further aspect of these proposals relates to methods of forming materials, layers, coatings or sheets as described herein, the method comprising intimately mixing MoS2 nanoflowers with PVDF in a solvent to form a mixture; and then removing the solvent from the mixture.
The present proposals relate to provision of robust, flexible piezoelectric and piezocatalytic materials formed from MoS2 nanoflowers embedded throughout a body comprising PVDF.
Nanoflowers are a known morphology for some materials. As discussed herein, nanoflowers are a known structural formation having multiple sheets of material joined together and which, at a microscopic level, have the appearance of flowers. Nanoflowers differ significantly from “nanosheets” or “few-layer sheets” due to the larger scale arrangement of the sheet-like petals. Nanoflowers typically have a higher surface area to volume ratio than “nanosheets” or “few-layer sheets”. Nanoflower morphologies are known for a range of materials, including MoS2.
As discussed herein, piezoelectric behaviour is the induction of electric charge in a solid material upon application of mechanical stress. Piezoelectric materials are ones demonstrating this behaviour. Piezoelectric behaviour differs from triboelectric behaviour which relates to generation of electric charge on separation of a material from another material with which it has been in frictional contact. The materials of the present proposals are preferably piezoelectric and not triboelectric.
As discussed herein, piezocatalytic behaviour (or piezocatalysis) is the induction of catalytic activity at the interface between a solid piezoelectric material and its environment, typically an aqueous environment, resulting in catalysis of a reaction that does not typically occur in the absence of the piezocatalytic material or when the piezocatalytic material is not placed under mechanical stress. Piezocatalytic behaviour is a subset of piezoelectric behaviour. Piezocatalytic behaviour is also dependent on surface morphology; it is not purely a piezoelectric phenomenon. Therefore, demonstration of piezocatalysis is not predicatble simply due to observance of piezoelectric behaviour. Piezocatalytic materials are ones demonstrating this behaviour. One common example of piezocatalytic behaviour, and a preferable property of the materials described herein, is the degradation of water where the free charges formed at the aqueous interface in turn generate reactive oxygen species (ROS) including .OH, .O−, .HO2 and H2O2 by local micro-electrolysis of water. The ROS generated by mechanical actuation of piezoelectric materials thus can be efficiently used to piezocatalytically oxidize and degrade contaminants in the aqueous environment, such as toxic and/or carcinogenic dyes and microbes in water from textile, chemical, pharmaceutical and food industries.
In the present proposals the MoS2 nanoflowers are preferably formed from >80 wt. % MoS2, preferably >90 wt. % MoS2, preferably >95 wt. % MoS2, preferably >99 wt. % MoS2, most preferably >99.9 wt. % MoS2.
The MoS2 nanoflowers are preferably broadly spherical in shape. Preferably the individual MoS2 sheets (or “petals”) are typically between 1 and 10 nm in thickness. Each MoS2 nanoflower preferably has a diameter up to 1 μm; preferably up to 800 nm, preferably up to 750 nm, preferably up to 500 nm. In some cases, each nanoflower preferably has a diameter in the range 10 nm-1 μm; preferably 50 nm-1 μm; preferably 200 nm-1 μm, preferably 500 nm-1 μm.
The MoS2 nanoflowers are preferably formed by a hydrothermal process.
Poly vinylidene difluoride (PVDF) is a polymeric material that is known to have multiple different crystalline phases α, β, γ and δ some of which demonstrate piezoelectric activity. The α phase is the most stable, is non-polar and does not exhibit piezoelectric behaviour. The β and γ phases are both polar due to the arrangement of the fluorine groups in the polymer chains, and do exhibit piezoelectric behaviour. In the present proposals the PVDF is preferably in the β form. Preferably the PVDF in the present materials is >60 wt. % β phase PVDF, preferably >70 wt. %, preferably >75 wt. %, preferably >80 wt. %, preferably >85 wt. %, preferably >90 wt. %.
The PVDF used in the present proposals is preferably not “poled” or subjected to a poling step before combination with the MoS2 nanoflowers, i.e. the PVDF is “self-poled” by combination with the MoS2 nanoflowers. In some cases the PVDF is preferably not subjected to electrospinning during the formation of the material. Preferably the poling of the PVDF in the material is achieved solely by self-poling due to interaction of the MoS2 nanoflowers and PVDF. For example the poling of the PDVF is preferably not achieved by addition of dopant materials in addition to the MoS2 nanoflowers.
Without being bound by theory, the self-poling property may occur through either hydrogen bonding or electrostatic interaction between Mo—S dipole in non-centrosymmetric MoS2 nanoflowers and positive-CH2 dipole of the polymer which induces β phase crystallization by orienting the polymer in a (trans, trans, trans, trans) “TTTT” conformation as shown in
The PVDF used in the present proposals preferably has a mass average molecular weight (Mw) determined by Gel Permeation Chromatography (GPC), in the range 50,000-800,000; preferably 100,000-500,000, preferably 100,000-250,000, preferably 150,000-200,000, preferably about 180,000.
The PVDF used in the present proposals preferably has a number average molecular weight (Mn) determined by GPC, in the range 10,000-200,000; preferably 20,000-150,000, preferably 35,000-100,000, preferably 50,000-100,000, preferably about 71,000.
The present proposals relate to a material in which MoS2 nanoflowers are combined with PVDF. The MoS2 nanoflowers are embedded throughout the PVDF body; they are not confined to a discrete layer or region within the material. Preferably the distribution of MoS2 nanoflowers though the PVDF is substantially uniform (as shown in
The present materials necessarily contain some level of MoS2 nanoflowers to achieve the desired effects. Preferably the materials contain up to about 20 wt. % MoS2 nanoflowers. Above about 20 wt. % the material can start to shed MoS2 nanoflowers on physical manipulation (e.g. bending, friction with adjacent materials etc.). This can be detrimental in applications such as water remediation where shedding of MoS2 nanoflowers into the water presents additional contamination of the water and is problematic to remove. Preferably the material contains up to about 20 wt. % MoS2 nanoflowers based on the weight of MoS2 nanoflowers and PVDF, preferably in the range 5-20 wt. %, preferably in the range 10-20 wt. %, preferably in the range 10-15 wt. %, preferably about 10 wt. %. Formation of β phase PVDF starts to occur at and above about 5 wt. % MoS2 content, below 5 wt. % the amount of β phase PVDF observed is very low.
In some cases, the PVDF may be present as a component in a co-polymer or a polymer mixture. For example the PVDF may be present as part of a copolymer system with a second polymer, preferably a piezoelectric polymer. In some cases the PVDF is present as part of a copolymer system selected from PVDF-HFP (poly(vinylidene fluoride-co-hexafluoropropylene)) and PVDF-TrFE (polyvinylidene fluoride-trifluoroethylene).
The present materials, preferably include at least 50 wt. % PVDF based on the weight of the total material; preferably at least 75 wt. %, preferably at least 80 wt. %, preferably at least 85 wt. %, preferably about 90 wt. %, preferably about 95 wt. %.
In aspects where PVDF is present as part of a copolymer system, the present materials, preferably include at least 50 wt. % PVDF copolymer based on the weight of the total material; preferably at least 75 wt. %, preferably at least 80 wt. %, preferably at least 85 wt. %, preferably about 90 wt. %, preferably about 95 wt. %.
In some preferred cases, the material consists of only MoS2 nanoflowers and PVDF; or consists essentially of only MoS2 nanoflowers and PVDF (i.e. other components are negligible contaminants having no significant effect on the properties of the material).
In the present proposals the MoS2 nanoflowers are embedded throughout a body comprising poly vinylidene difluoride (PVDF). In preferred cases, the body consists of, or consists essentially of, PVDF or a PVDF copolymer, preferably PVDF.
In the present materials, the provision of MoS2nanoflowers embedded throughout a body comprising PDVF results in a material that demonstrates piezoelectric properties and piezocatalytic properties.
Typically the MoS2 nanoflowers and PVDF interact in a synergistic manner to provide one or both of piezoelectric and piezocatalytic activity at a higher level that would be expected from the properties of MoS2 nanoflowers and PVDF alone and from the properties of known materials containing MoS2 in other morphologies and PVDF. This synergistic behaviour may, for example, manifest in one or more of, particularly high piezoelectric voltage for a given pressure, particularly effective piezocatalytic behaviour, particularly robust materials, and particularly long-lasting piezocatalytic behaviour.
While composite materials of few-layer MoS2 sheets and PVDF are known, these do not display piezocatalytic properties; they do not, for example, degrade dyes in an aqueous environment as effectively as the materials of the present proposals. Furthermore, the piezoelectric properties of such known systems are significantly worse than the materials of the present proposals. For example the piezoelectric open-circuit voltage under for a given mechanical stress is significantly higher for the materials of the present proposals than for those in which MoS2 sheets are used in combination with PVDF.
While composite materials of MoS2 nanoflowers and PDMS are known, these do not display piezoelectric properties; displaying instead triboelectric activity. Furthermore the open-circuit voltage generated is significantly higher for the materials of the present proposals than for those in which MoS2 nanoflowers are used in combination with PDMS. In addition, the composite materials of MoS2 nanoflowers and PDMS degrade with repeated use as compared to those of the present proposals which retain piezocatalytic behaviour over at least 10 cycles of water treatment.
While layered materials comprising a MoS2 nanoflower layers sandwiched between electrospun PVDF layers are known, the piezoelectric properties of such known systems are significantly worse than the materials of the present proposals. For example the piezoelectric open-circuit voltage under for a given mechanical stress is significantly higher for the materials of the present proposals than for those in which MoS2 nanoflower layers sandwiched between electrospun PVDF layers. Furthermore the electrospinning of the PVDF layers that is required to achieve poling in these known systems, adds complexity and energy requirements to the manufacturing steps and limits the shape and applications of devices formed from the material.
The materials of the present proposals may contain other components alongside the MoS2 nanoflowers and PVDF. Such other components, if present, are selected so as not to negatively impact the piezoelectric and piezocatalytic properties of the materials. The other components are not particularly limited and may include one or more of the following, colourants, stabilisers, and fillers. Surface coatings applied over the material may act as a barrier to the interaction of the material with the environment so are preferably avoided.
The materials described herein may be used to form a variety of structures. Preferably the materials herein are used to form a coating, layer or sheet. Such thin structures are preferred, particularly for energy harvesting applications because they are typically flexible meaning that they can be easily incorporated into products that experience high levels of mobility during use, e.g. energy harvesting clothing. Many piezoelectric materials are relatively rigid solids, e.g. ceramics, so this flexibility provides a significant advantage in such products because it avoid imparting unwanted rigidity into the product. In some cases, the materials described herein are preferably prepared as a coating, layer or sheet, optionally on an electrically inert substrate. Optionally the coating, layer or sheet has a thickness of 2 mm or less, preferably 1 mm or less, preferably 750 μm or less, preferably 500 μm or less, preferably 250 μm or less, preferably 100 μm or less, preferably about 50 μm. In some cases it is preferred to have a lower limit on the thickness of about 1 μm, preferably about 10 μm, preferably about 25 μm. Optionally, a coating, layer or sheet as described herein may be used with a suitable adhesion promoter or primer, e.g. as a backing layer, to improve adhesion and robustness.
An advantage of the present materials is that they can be used to form products of essentially any shape by using a casting process. For example monolithic structures can be formed that have piezoelectric and piezocatalytic properties. The materials described herein can be used in this way because they have a uniform composition throughout the material. They are also formed from a uniform mixture by a casting process. In the materials described herein, a specific arrangement of components, e.g. layers of MoS2 particles sandwiched between PVDF sheets, is not required to achieve the desired piezoelectric and piezocatalytic properties. This represents a significant advantage of the materials described herein.
The materials described herein demonstrate beneficial piezoelectric properties, for example:
In some preferred aspects the materials described herein demonstrate one, two or all three of the preferred piezoelectric characteristics 1-3 listed above.
The materials described herein demonstrate beneficial piezocatalytic properties, for example:
The materials described herein offer particular benefits in water remediation, i.e. removal of contaminant species from aqueous environments. This is demonstrated by the excellent activity in removal of Ethidium bromide, Eosin Y, Rhodamine B and Acridine Orange dyes. To date, degradation of these dyes has been mainly limited to using photocatalytic nanoparticles (such as ZnO, TiO2, SnO2, Fenton's reagent, Au and Ag) under light irradiation. In contrast, the MoS2-PVDF materials described herein achieve this degradation through a fast-piezocatalytic process which harnesses vibrational energy to degrade the dyes under dark conditions. Such activity is suitable, for example for treatment of industrial effluents flowing through pipelines.
The present proposals also relate to the preparation of a piezoelectric and piezocatalytic device using the materials described herein. Such a device may be formed by providing a sheet of the composite MoS2-PVDF composite material described herein and sandwiching between two electrodes. These electrodes can be as simple as pieces (e.g. sheets) of electrically conducting material that act as a conduit for the electrical charges that build up at the surfaces of the composite material during mechanical stressing. Preferably the electrodes are formed from two sheets of electrically conducting material selected from copper, aluminium, silver, and gold, each having a wire in electrical contact with it to conduct the electrical charge away from the device.
The present proposals also relate to the use of materials, layers, coatings, sheets and devices as described herein for piezocatalytic removal of contaminants from an aqueous environment. For example by placement in an aqueous environment in need of remediation and subsequently applying mechanical stress, preferably repeatedly applying mechanical stress. Examples may include removal of contaminants from industrial effluent, e.g. by placement on an interior surface of an industrial effluent pipe, removal of contaminants from drinking water, removal of pathogens such as harmful microbes, from water that is to be used for drinking or washing.
Methods of piezocatalytic removal of contaminants from an aqueous environment also form part of the present proposals, the methods comprising contacting the aqueous environment with a material, layer, coating, sheet or device as described herein, and applying mechanical stress to said material, layer, coating, sheet or device.
The present proposals also relate to the use of materials, layers, coatings, sheets and devices as described herein for generation of piezoelectricity. For example use in the harvesting of energy from mechanical motion. In some cases this may be incidental mechanical motion, i.e. motion that is inherent in the system and not deliberately applied or induced solely for the purpose of energy generation. For example incorporation into clothing to harvest energy from human body motion, harvesting energy from ambient vibrations in the environment, e.g. acoustic vibrations, harvesting energy from liquid flowing over the nanocomposite, harvesting energy from impact and tapping forces.
Methods of generating piezoelectricity also form part of the present proposals, the methods comprising providing a material, layer, coating, sheet or device as described herein, and applying mechanical stress to said material, layer, coating, sheet or device.
Methods of forming materials as described herein also form part of the present disclosure, the methods comprising intimately mixing MoS2nanoflowers with PVDF in a solvent to form a mixture; and then removing the solvent from the mixture. In these methods, the solvent is not particularly limited; it is preferably selected from dimethyl sulfoxide (DMSO), DMF (dimethyl formamide), NMP (N-methyl pyrollidone), and DMAc (Di methyl acetamide), preferably it is DMSO.
The step of intimately mixing the MoS2 nanoflowers with PVDF is not particularly limited as long as it achieves a reasonably uniform distribution of the MoS2 nanoflowers throughout the body of PVDF; simple stirring to achieve complete dispersion of the MoS2 nanoflowers is preferred.
The methods may also include a step prior to removal of the solvent, of placing the mixture into a mold or applying as a layer to a surface. This allows formation of any desired shape of the material; something that is not achievable with some known piezoelectric and/or piezocatalytic materials, particularly where the known materials use layered structures. Preferably the methods include a step of applying the mixture as a layer on a surface prior to removal of the solvent.
The removal of solvent may be achieved by one or more of heating, reducing pressure, or simply leaving the solvent to evaporate under ambient temperature and pressure. In some cases, particularly for thin layers, the step of removing the solvent from the mixture is passive, i.e. simply leaving the solvent to evaporate under ambient temperature and pressure. In some cases the step of removing the solvent comprises heating, e.g. heating to a temperature in the range 50-100° C., such as 80° C. under ambient pressure. Removal of solvent by heating typically results in higher levels of β phase PVDF formation than evaporation at ambient temperature, therefore removal of solvent by heating is preferred.
Preferably the methods do not include a step of electrospinning. Preferably the methods do not include a step of electrospinning of the PVDF. Preferably the present methods do not include a step of poling the PVDF before combination with the MoS2 nanoflowers, i.e. the step of combining the PVDF with the MoS2 nanoflowers results in “self-poling” of the PVDF. For example the methods preferably do not include the addition of dopant materials in addition to the MoS2 nanoflowers to PDVF.
The following Examples are provided by way of illustration of the present proposals and do not limit the present disclosure.
Physico-chemical characteristics including phase formation, microstructure, elemental distribution and thermal properties of MoS2 nanoflower and MoS2-PVDF film was performed using X-ray diffraction (XRD; Model-D8, Bruker AXS Inc., Madison, Wis.), Fourier transform infrared (FTIR) spectroscopy (FTIR-84005, Shimadzu), Field emission scanning electron microscopy (FESEM; INSPECT F50, Netherlands), Energy dispersive x-ray analysis (EDAX) and Differential scanning calorimetry (DSC-60, Shimadzu). Ferroelectric properties of the film were measured in terms of polarization-electric field (P-E loop) using Hysteresis version 4.9.0 (Radiant technologies).
Open circuit voltage (Voc) generated by the MPNG under continuous finger imparting and ultrasound was measured using a digital storage oscilloscope (Keysight, Oscilloscope DSO-X 3012A). Short circuit current (Isc) was recorded under the same condition using Keysight, Electrometer B2985.
Catalytic degradation of dyes was monitored using a UV-Visible spectrophotometer (Lambda 650, Perkin Elmer) and .OH was measured with terephthalic acid (Merck, Germany) using a Cary Eclipse Fluorescence spectrophotometer (Agilent Technologies).
Synthesis of MoS2 Nanoflowers
MoS2 nanoflowers were synthesized by hydrothermal process. 0.28 g of Pluronic F-127 (Merck, Germany) was dissolved in 140 mL of distilled water. Next 8.5 g of Ammonium heptamolybdatetetrahydrate, (NH4)6Mo7O24.4H2O, (Merck, Germany) and 1.28 mg Thiourea, CH4N2S, (Merck, Germany) were added to the solution and stirred at room temperature for 30 min. The resulting homogeneous solution was then loaded in a stainless-steel Teflon lined hydrothermal reactor and was kept in an oven at 200° C. for 24 h. After the reaction, the black precipitate was centrifuged and washed with water and alcohol repeatedly. The precipitate was then dried to get a free-flowing powder and stored for further characterization and use.
Synthesis of MoS2-PVDF Films
MoS2 nanoflower doped PVDF film was fabricated using solution processing. 250 mg of PVDF (Sigma-Aldrich, Germany; Mw: 180,000 GPC; Mn: 71000) was dissolved in 60 mL of Dimethyl sulfoxide (DMSO) (Merck, Germany) under constant magnetic stirring at 60° C. to obtain a homogeneous solution. Next, MoS2 (10 wt % of PVDF) powder was added to the PVDF solution and continuously stirred at room temperature until complete dispersion was achieved. Afterwards, the colloidal suspension was transferred to a clean petri dish and dried at 80° C. in an oven to produce a nanocomposite film.
For comparison, pure PVDF film was also prepared in the same way but without MoS2 nanoflowers.
XRD Analysis
The XRD pattern of pure MoS2 and the MoS2-PVDF film prepared in Example 1 is shown in
MoS2 shows characteristic broad reflections at 13.97° (002), 33.66° (102), 39.97° (103), 49.94° (105) and 59.41° (110) which confirms phase formation in the as synthesized powder.
In the MoS2-PVDF film, addition of MoS2 nanoflowers significantly promotes nucleation of polar electroactive β-crystals in PVDF film which is indicated by a sharp single peak at 2θ=20.5° ((110), (200)) and absence of a phase reflections. In addition, reflections corresponding to MoS2 are also present indicating the composite nature of the film.
FTIR Analysis
FTIR spectra of the pure MoS2 and the MoS2-PVDF films formed as in Example 1 shown in
Pure PVDF (lower spectrum in
In case of MoS2-PVDF (upper spectrum in
The fraction of electroactive β phase content in the nanocomposite MoS2-PVDF film was calculated by using the Lambert-Beer Law. Using this equation, the β phase crystallization in pure PVDF is found to be 30% whereas for MoS2-PVDF it reached 80%. Since the piezoelectric nature of PVDF is strongly dependent on the amount of electroactive β phase, therefore the addition of MoS2 nanoflowers clearly enhances its piezoelectric properties.
DSC Thermograph Analysis
The phase crystallization and melting behavior of pure PVDF and MoS2-PVDF film formed as set out in Example 1 was also analyzed by differential scanning calorimetry (DSC) to complement XRD and FTIR measurements. Results are shows in
The melting peak at 164.5° C. in the DSC thermograph of pure PVDF film indicates presence of nonpolar a polymorph, whereas for the MoS2 nanoflower-doped PVDF, the melting peak is shifted to a higher temperature indicating the nucleation of electroactive β phase in the nanocomposite film. The enthalpy of fusion and crystallinity both increased upon MoS2 nanoflower doping; MoS2-PVDF film had Xc≈53.43% compared to Xc≈33% for pure PVDF. This change is due to interaction between MoS2 nanoflowers and the polymer resulting in the formation of β-crystals in the nanocomposite film.
Field Emission Scanning Electron Microscopy (FESEM) Imaging
The morphology of the piezoelectric films formed as set out in Example 1 was assessed by FESEM and representative images shown in
MoS2-PVDF material (formed as in Example 1) shows distinct formation of spherulites of diameter ˜5-8 μm which confirms β phase crystallization (
MoS2-PVDF Nanogenerator (MPNG) Fabrication
A nanogenerator was fabricated by using an MoS2-PVDF film of dimension 1 cm×1 cm×50 μm formed as set out in Example 1. A 40 μm thick copper/aluminium electrode was attached to each side of the film and with a copper wire attached to each electrode. Next, the film containing the electrodes and connecting wires was packaged in polydimethylsiloxane (PDMS) (Sylgard 184, Dow Corning, ratio of 1:10) by immersing the nanocomposite films in PDMS gel and drying for 15 min in a vacuum followed by drying at 60° C. for 1 h to remove bubbles from the mixture. The final package size of the as-fabricated MPNG device was 2 cm×2 cm×0.3 cm.
Ferroelectric Characterization
Ferroelectric properties of MoS2-PVDF film formed as set out in Example 1 were determined from the room-temperature polarization-electric field (P-E) hysteresis loop measurements at 50 Hz in the ±200 kV/cm range. The area within the loop corresponds to heterogeneous charge density and indicates charge storage capability of the material. As can be seen from
The piezoelectric coefficient (d33) of MoS2-PVDF is calculated to be −36.4 pC/N. This value is higher than observed in poled PVDF (−24 pC/N) showing that the composite film has superior piezoelectric properties to poled PVDF but without undergoing any specific poling step.
A strain vs field curve was also plotted for MoS2-PVDF and is shown in
The characterisation of the MoS2-PVDF film confirms the self-poling that is inherent in the formation method and confirms the piezoelectric behaviour feature of the MoS2-PVDF nanocomposite.
MoS2-PVDF Nanogenerator (MPNG) Performance
The piezoelectric output of the MPNG device under periodic human finger tapping (˜5 Hz) is shown in
The variation of the output voltage from MPNG was further evaluated across different load resistances (ranging from 1 to 40 MΩ); the instantaneous voltage increased and gradually reached a peak value of 84 V at 30 MΩ similar to open voltage circuit (Voc) (
To demonstrate the application potential of the MPNG of Example 4, it was connected to a 1 μF capacitor through a bridge rectifier. As shown in
A comparison of the MPNG device of Example 4 with other previously reported PVDF based nanogenerators is summarized in table 1.
A pure PVDF-based nanogenerator produced only 4V under the same tapping force.
A comparison of capacitor charging ability of the MPNG device of Example 4 with other previously reported PVDF based nanogenerators is also summarized in table 2.
Piezcatalysis Characterisation
A MoS2-PVDF nanocomposite film formed according to Example 1, having dimensions 2 cm×2 cm and thickness 50 μm was immersed in 10 mL of 10 ppm solutions of each of the following dyes (all Loba chemie) in deionised water.
The conical flask containing the dye solution and the nanocomposite film was placed in a bath sonicator (RS Pro Ultrasonic Cleaner, 100W) and subjected to pulsed ultrasonic vibrations for 20 mins. A small portion of the dye solution was pipetted out at regular intervals (0, 5, 10, 15 and 20 min) and measured using UV-Visible spectrophotometer to check degradation. The percent degradation and the rate constant were calculated from the measured data.
A recyclability test was also performed with Rhodamine B which included 10 cycles of catalytic tests using 200 mL of 10 ppm dye concentration to determine the efficacy of the MPNG film for treating large volumes of water.
All the catalytic experiments were carried out in dark at 25° C.
Piezocatalytic Dye Degradation
Piezocatalytic dye degradation was monitored using UV-Visible spectroscopy. Results are presented in
As can be seen all dyes showed rapid degradation within 20 minutes of ultrasonication with the nanocomposite MoS2-PVDF film formed as in Example 1 under in dark conditions. The degradation was also visually observed from the change in dye colour after 25 minutes of ultrasonication thereby clearly demonstrating piezocatalytic activity.
In contrast, pure PVDF film failed to any appreciable degradation of dyes even after prolonged sonication (50 mins).
The percent degradation over time is presented in
The degradation reaction followed pseudo first order kinetics as indicated from the rate of degradation curve (
Terephthalic acid forms a fluorescent hydroxyterephthalic acid upon reaction with .OH radical, which offers qualitative means to detect the radical formation with high sensitivity.
To assess lifetime of the MoS2-PVDF film formed as in Example 1 the piezocatalysis test was repeated using the same film with fresh solution of Rhodamine B (200 mL, 10 ppm) on each repetition. The result presented in
Number | Date | Country | Kind |
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2010854.4 | Jul 2020 | GB | national |
Filing Document | Filing Date | Country | Kind |
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PCT/EP21/69531 | 7/13/2021 | WO |