Separation of metal-organic frameworks
10899777 ยท 2021-01-26
Assignee
Inventors
- Marta Rubio Martinez (Clayton South, AU)
- Pablo Juliano (Clayton South, AU)
- Thomas Leong (Clayton South, AU)
- Matthew Roland Hill (Clayton South, AU)
- Kok Seng Lim (Clayton South, AU)
Cpc classification
B01D21/283
PERFORMING OPERATIONS; TRANSPORTING
B01J20/226
PERFORMING OPERATIONS; TRANSPORTING
B01D2253/204
PERFORMING OPERATIONS; TRANSPORTING
C07B63/00
CHEMISTRY; METALLURGY
B01J20/30
PERFORMING OPERATIONS; TRANSPORTING
B01J20/305
PERFORMING OPERATIONS; TRANSPORTING
International classification
B01J20/28
PERFORMING OPERATIONS; TRANSPORTING
C07B63/00
CHEMISTRY; METALLURGY
B01D21/28
PERFORMING OPERATIONS; TRANSPORTING
Abstract
A method of separating a metal organic framework (MOF) from a solution and associated apparatus. The method comprises: providing a MOF containing solution; contacting the MOF containing solution with an acoustic reflector surface such that, any high frequency ultrasound applied within the MOF containing solution reflects off the acoustic reflector surface; and applying a high frequency ultrasound of at least 20 kHz to the MOF containing solution. The MOF material is substantially separated from solution as aggregated sediment that settles out of solution.
Claims
1. A metal organic framework separation apparatus that separates a metal organic framework (MOF) from a MOF containing solution, comprising: a housing having a reservoir that receives the MOF containing solution; a high frequency ultrasound transducer operatively connected to the reservoir that applies megasonic frequencies of at least 20 kHz to the MOF containing solution; and an acoustic reflector surface spaced apart from the transducer within the housing; wherein the transducer, in use, being operated to reflect said applied high frequency ultrasound off the acoustic reflector surface, said acoustic reflector surface being spaced away from the high frequency ultrasound transducer such that a standing wave is formed by the superimposition of a reflected sound wave to form pressure nodes and antinodes where particles are collected, wherein the standing wave causes the MOF content of the MOF containing solution to separate out from the MOF containing solution as an aggregated sediment.
2. The apparatus according to claim 1, wherein the applied high frequency ultrasound is 20 kHz to 4 MHz.
3. The apparatus according to claim 2, wherein the high frequency ultrasound transducer comprises a plate transducer.
4. The apparatus according to claim 1, wherein the housing comprises a container including at least one wall position to contact the MOF containing solution, and the transducer is high frequency ultrasound transducer is position within the reservoir or in engagement with the at least one wall.
5. The apparatus according to claim 1, wherein the acoustic reflector surface is generally located in front of the transducer, and spaced apart from that transducer.
6. The apparatus according to claim 1, wherein the housing includes at least one reflector surface that reflects the applied megasonic frequencies within the reservoir.
Description
BRIEF DESCRIPTION OF THE DRAWINGS
(1) The present invention will now be described with reference to the figures of the accompanying drawings, which illustrate particular preferred embodiments of the present invention, wherein:
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DETAILED DESCRIPTION
(19) The present invention provides a new separation apparatus, system and method that can separate a metal-organic framework (MOF) from a solution. The method has also been found to purify the MOF, removing contaminants from the pores of the MOF and also improve the surface area of the treated MOF, producing a purified MOF having a higher surface area than comparable commercially available samples.
(20) In this regard, the Inventors have surprisingly found that the use of ultrasonic and/or megasonic frequencies not only separates MOF material/particles from other components in a solution, but also purifies and activates the separated MOF. A MOF is extremely porous and therefore contaminant species in a solution can be trapped or otherwise located in these pores. The method, system and apparatus of the present invention have been found to substantially remove any contaminants from the pores of MOF material treated with the megasonic method and apparatus. This produces a desirable substantially pure MOFs which is highly scalable.
(21) Furthermore, the Inventors have also surprisingly found that the use of ultrasonic, preferably megasonic frequencies also improves the surface area of the final product, acting as an alternate process to the time consuming and costly calcinations traditionally used for surface area improvement. The process can therefore assist in maintaining MOF product quality i.e. porosity, thermal and chemical stability.
(22) The present invention can therefore permit large-scale production of MOFs at drastically reduced costs, allowing commercialisation of these MOFs for many potential real world applications. The present invention provides a fast, cost-effective, lowered environmental impact strategy to produce high-quality MOFs at a large scale.
(23) The present invention uses megasonics technology for separation and activation of metal organic frameworks. The Inventors believe that this is the first time that ultrasonic frequencies and more particularly megasonic frequencies have been used for the separation of MOFs. Furthermore, the Inventors believe that this is the first time that megasonics has been used for the purification/activation of porous materials, and in particular MOFs.
(24) Separation according to the present invention applies >20 kHz, in some cases >400 kHz, preferably between 20 kHz to 4 MHz, preferably 500 kHz to 2 MHz, more preferably between 800 kHz and 2 MHz, and yet more preferably between 1 MHz and 2 MHz high frequency ultrasound to create a standing wave, i.e. regions of minimal pressure (nodes) and maximal pressure (antinodes) within a liquid filled separation chamber. Whilst not wishing to be limited to any one theory, the Inventor's consider that when using this method, suspended particles or droplets migrate specifically towards one of these two regions due to acoustic radiation forces, based on their density and compressibility. In general, the aggregated MOFs are slightly denser than the surrounding fluid, and migrate towards the pressure nodes. This gathering of MOF material enhances the tendency to form larger aggregates which then sediment at a greatly accelerated rate to the bottom of the separation chamber, where they can be collected.
(25) The process and apparatus of the present invention also has the ability to achieve specificity of separation based on particle size by tuning of the operation parameters such as frequency and energy density.
(26) Furthermore, the application of the sound waves dramatically enhances the rate of separation, and hence reduces the chemical requirement and environmental footprint of conventional separation processes such as flocculation and sedimentation. This can be seen in a comparison of cleaning and separation techniques shown in Table 1:
(27) TABLE-US-00001 TABLE 1 Comparison of cleaning and separation techniques using MIL-53 as a control MOF Activation Temperature SA.sub.BET Methods Separation time ( C.) (m.sup.2/g) Centrifuge.sup.1 Yes 1 min Room Temp 806 Megasonics.sup.1 Yes 10 min Room Temp 1183 Ultrasound in the No 40 min 70 787 presence of Amides .sup.2 Ultrasound in the No 1 hour 70 1425 presence of Amides .sup.2 Supercritics.sup.3 Yes 4 hours 250 C. and 100 bar 1010 Calcination .sup.2 No 72 hours 325 1256 .sup.1Applicant's experiments. .sup.2 M. Gaab, N. Trukhan, S. Maurer, R. Gummaraju and U. Mller, Microporous Mesoporous Mater., 2012, 157, 131-136. .sup.3P. A. Bayliss, I. A. Ibarra, E. Prez, S. Yang, C. C. Tang, M. Poliakoff and M. Schrder, Green Chem., 2014, 16, 3796.
(28) Ultrasonics and/or megasonic operation involves no moving parts, and can have a low surface area of contact with the fluid providing a lower capacity for fouling, and ease of cleaning. A separator according to the present invention essentially comprises a housing or container in which a liquid reservoir can be formed. The liquid reservoir is filled with a MOF containing solution. A high frequency transducer, such as a plate transducer is either submerged in the liquid filled reservoir or engaged with a wall of reservoir to project megasonic frequencies through the MOF containing solution for a certain length of time to effects the desired separation of MOF from solution and/or separation of contaminants from the MOF into the solution.
(29) The Applicant considers that the size, material and/or geometry of the reactor vessel may have an effect on the outcome (degree, efficiency or the like) of the separation process of MOFs using the present invention. Similarly, the positioning, arrangement and alignment of transducers within a separation apparatus may have an effect on the outcome (degree, efficiency or the like) of the separation process of MOFs.
(30) The Applicant notes that ultrasonics and megasonics are a well know separation technique for particles, particularly in the biotechnology and food processing areas. Previous applications of ultrasonics and megasonic involved liquid/liquid and solid/liquid separation especially in food processing (milk fat separation and palm oil separation). However, the Inventors are not aware of any previous published work using ultrasound, in particular megasonics, for the combined separation, washing, and/or activation of any porous material.
(31) The inventors believe that the ultrasonic and megasonic ranges of the present invention provide at least one of surface area improvement, separation and/or washing properties for MOF containing solutions. The difference between ultrasonic and megasonics lies in the frequency that is used to generate the acoustic waves. Ultrasonic uses lower frequencies (20 kHz to 400 kHz) and produces random cavitations. Megasonic uses higher frequencies frequency (>0.4 MHz to several MHz) and produces controlled and smaller cavitations which allows the separation of nanocrystals (in our case, the MOFs). Furthermore, higher megasonic frequencies do not cause the violent cavitation effects found with ultrasonic frequencies. This significantly reduces or eliminates cavitation erosion and the likelihood of surface damage to the product being cleaned.
(32) Again, it should be appreciated that the MOF containing solution typically comprises a mixture or suspension of the MOF particles within the solution. In this regard, the MOF comprises a solid component or particles which are dispersed throughout the liquid of that solution. For ease of reference, this suspension of MOF particles in solution will be referred to as a MOF containing solution in this specification.
(33) The separation method and apparatus of the present invention utilises a reflector within the separation arrangement. Without wishing to be limited to any one theory, the Inventors have found that introducing a reflector allows a standing wave to be formed through constructive interference. As the soundwaves from the transducer reach the reflector, they are reflected where they may interact with the original transmitted wave. If the reflected and the transmitted wave are in phase, i.e. the peaks and troughs of the waves are aligned, then constructive interference will occur leading to resonance. With this occurrence, pressure nodes and anti-nodes will form along the path of the interacting sound waves at distances equal to multiples of half the wavelength of the waves.
(34) Particles in the vicinity of these nodes and anti-nodes experience a series of forces as a result of the sounds resonance, these are known as the primary acoustic radiation force and the Bejerknes force (or secondary acoustic radiation force). These forces will cause the solid MOF species to agglomerate at the nodes or anti-nodes, increasing the rate of settling (given their density is greater than the fluid). After time, the solids will deposit within a bed forming solids lean supernatant.
(35) Acoustic cavitation within a liquid is a possibility when operating with megasonics; the intense pressure of the ultrasonic waves has the capability to cause dissolved gases to exit solution leading to the formation of bubbles. Upon collapsing, extreme temperatures and pressures can be achieved of up to 10,000 K and many hundreds of bar respectively.
(36) Increasing the ultrasounds frequency has the effect of smaller bubbles as they collapse faster under the more intense conditions. These smaller bubbles collapse with less energy, leading to less cavitation. The range of ultrasonic frequencies over which cavitation can be observed is typically between 20 kHz to 4 MHz.
(37) The primary acoustic radiation force (F.sub.ac) is a second order, non-linear force that acts upon particles within an acoustic standing wave field. Momentum is transferred from the soundwave to the solid, allowing its manipulation in the direction parallel to the soundwaves propagation. For an ideal standing wave, the time averaged force in the direction of the sounds propagation can be described by:
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(39) Where: R Is the Particle Radius k is the wavenumber E.sub.ac is the specific energy density is the acoustic contrast factor .sub.m, .sub.p is the density of the medium or particle respectively .sub.m, .sub.p is the compressibility of the medium or particle respectively
(40) The compressibility of the particle can be estimated from the following relation:
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(42) The acoustic contrast factor determines whether the solids will be driven to the nodal or anti-nodal planes of the resonance field. A negative factor (<0) indicates the particles will be displaced to the pressure anti-nodes within the field, whilst a positive factor (>0) indicates the particles will be displaced to the pressure node planes (see
(43) The secondary acoustic radiation force (F.sub.sec), also known as the Bejerknes force acts upon the particles within the nodal plane pushing them towards each other and resulting in aggregation. Outside of the nodal planes, at angles other than 90, the particles are repulsed as shown in
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(45) The force results from the scattering of the sound waves from neighbouring particles within a sound field.
(46) Transducer alignment needs to be considered in the positioning of the transducer 40 and reflector 42 within a housing 44 of a separation apparatus according to the present invention to generate standing waves. A vertical or horizontal alignment between the transducer 40 and reflector 42 refers to whether the transducer 40 or reflector 42 is positioned in a way that the nodal/antinodal bands are aligned in the vertical or horizontal plane (see
(47) Where gravity is a necessary mechanism for enhanced separation (i.e., product collects at the top or bottom of the container), a vertical alignment (see
(48) A horizontal alignment (see
(49) The Inventors have found that both types of alignments can be successfully applied for use of MOFs activation and separation. However, due to the above outlined reasons, the horizontal alignment requires additional time for settling the MOF crystals at the bottom of the vessel.
(50) Sound wave attenuation may also be a factor to consider during the separation process. As the wave propagates through the medium, its energy will dissipate into mainly the form of heat. The rate at which this attenuation occurs depends upon the medium (both the fluid and the suspended solid) which the sound is travelling through in addition to frequency. Higher frequencies experience more rapid attenuation in a media; hence lower frequencies may be favoured with care taken to avoid cavitation.
(51) In achieving separation, care must be taken to ensure the distance over which the sound must travel (to reflector and back) is not such that excessive attenuation occurs, resulting in weak acoustic separation forces. Whilst the volume which can be separated may increase with a larger separation distance between transducer and reflector, the rate of separation may be adversely affected in doing so. Sound wave attenuation is proportional to frequency, such that increasing the frequency will reduce the distance over which the separation will be effective.
(52) Particle size may also have significant effect upon the separation process given both the primary and secondary acoustic radiation forces are proportional to the cubed radius (Eqn. 2.1 and 2.5). Therefore a larger particle is more easily manipulated than a smaller particle; however particles that are too large could interrupt the standing field of the resonance wave.
(53) Acoustic streaming occurs when the fluid bulk is set in motion due to the sound wave oscillations which can overcome the manipulative acoustic radiation forces acting on the nodal and anti-nodal separation planes.
(54) Acoustic attenuation, amongst other mechanisms, tends to lead to the occurrence of acoustic streaming. Attenuation scales with square of the frequency of the sound wave, as described by:
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(56) Hence increasing the frequency and amplitude of the sound wave will result in more significant streaming which may severely hinder the separation process.
EXAMPLES
(57) The separation of two studied MOFs, aluminium fumarate (Al-fum) and aluminium terephthalate (MIL-53) using a Megasonic separation process and apparatus according the present invention, will now be exemplified by example. However, it should be appreciated that the present invention is suitable for use with a large number of MOFs and should therefore not be limited to the exemplified MOF structures in these examples. The examples provided can therefore be more generally applied to a wide range of MOFs.
Example 1MOF Separation
(58) MOF Synthesis
(59) Aluminium fumarate (Al-fum) and aluminium terephthalate (MIL-53) were synthesized using flow chemistry technology following the methodology taught in Rubio-Martinez et al, (2014) Versatile, High Quality and Scalable Continuous Flow Production of Metal-Organic Frameworks, Scientific Reports 4, Article number: 5443 doi:10.1038/srep05443 (Rubio-Martinez 2014), the contents of which are to be understood to be incorporated into this specification by this reference.
(60) Aluminium fumarate (Al-fum) and aluminium terephthalate (MIL-53) were used as each exhibit high thermal stability up to 450 C. and present a reversible uptake/release of water provided by an octahedral aluminium configuration and a strong AlO bond. Both of these MOFs present very similar structures where the carboxylate groups of the corresponding linkers lead to the formation of a 3D structure with rhombohedral channels interconnected by infinite AlOHAl chains.
(61) A schematic representation showing the general flow reactor setup for the production of MOFs generally following Rubio-Martinez 2014 is shown in
(62) In a typical reaction, two separate solutions of the precursors are pumped through a T-type static mixer to promote diffusion mixing of the reagent input streams. The combined reagent streams are then directed into the heated reactor zone of the Salamander Flow Reactor for a predetermined residence time. On exiting the reactor, the MOF stream 65 is cooled in an external heat sink unit, based on a coiled tube in a water bath (
(63) MOF stream 65 can be collected in a container or reservoir 70 which can then be subsequently fed into a megasonic separator 100 according to the present invention. This device is illustrated in more detail in
(64) Synthesis of Al-Fumarate
(65) The general procedure described above was employed. An aqueous solution of 0.35M Al.sub.2(SO4).sub.3 18H.sub.2O and an aqueous solution of 0.7M of fumaric acid and 2M of NaOH solution were mixed under continuous flow conditions and heated in a tubular reactor. The synthesis was conducted at 65 C. using a total flow rate of 90 mL.Math.min.sup.1, giving a total residence time of 1.2 min. The material was washed three times with fresh water and twice with ethanol and dried in vacuum (500 mbar) for 8 hours at 40 C. Yield: 100%.
(66) S2.b. Synthesis of MIL-53 (Al)
(67) The general procedure described above was employed. An aqueous solution of 0.08M Al(NO.sub.3).sub.3 and an aqueous solution of 0.08M of terephthalic acid and 0.24M of NaOH solution were mixed under continuous flow conditions and heated in a tubular reactor. The synthesis was conducted at 140 C. using a total flow rate of 90 mL.Math.min-1, giving a total residence time of 1.2 min. The material was washed three times with fresh water and twice with ethanol and dried in vacuum (500 mbar) for 8 hours at 40 C. Yield: 83%.
(68) MOF Separation Process
(69) The MOF crystals were isolated from the solvent using a megasonic apparatus and process according to one embodiment of the present invention. A conventional centrifuge was used as a control reference.
(70) The megasonic separator 100 is shown in
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(72) The illustrated clear polycarbonate 6-litre container is split into two sections, a 1.1 L treatment section 110 containing the transducer plate 105 and an unprocessed section 112. The treatment section 110 and unprocessed section 112 are separated by a metallic (stainless steel) reflector plate 115 used to reflect the megasonic waves.
(73) The plate transducer 105 was used for sonication at a frequency of 1 and 2 MHz (290 W) in separate trials for 10 min. Each experiment consisted of filling the acoustic reactor with a diluted MOF solution (50% in water) and immediately sonicating for 10 min. A control system, where no ultrasound was applied, was simultaneously filled with a portion of the same MOFs solution to observe the differences. In all experiments the temperature increased up to 10 C., caused by acoustic energy dissipation, therefore an ice bath is used during the experiments.
(74) Before and after the application of ultrasound, 10 mL samples were removed to measure the -potential of the MOFs. Using megasonics the MOF product was washed three times with fresh water and twice with EtOH.
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(77) The inventors believe that the precise mechanism may be related to changes in the local density that the aggregates experience due to varying size distribution of the nanosized MOF crystals. Generally, the influence of ultrasound on suspended particles depends on particle size, density and ultrasonic field. However, the resultant separation can be further influenced by possible interactions between MOF particles when they collide (i.e. surface properties). The solvent properties will also influence the specific density of the particles in the field, so that may also affect the separation efficiency as well. For the MOFs structures and solvent studied in these experiment, no appreciable differences were observed.
(78) To determine the quality of the crystals, the MOFs separated with megasonic treatment apparatus 100 and a standard lab-scale centrifuge were compared by XRPD and SEM measurements. X-Ray powder diffraction (XRPD) confirmed the crystallinity of Al-fum and MIL-53, showing identical patterns to those of crystals synthesized by solvothermal methods. Note that the Megasonics separation had no impact on the crystallinity of the materials as demonstrated by identical pattern diffraction (See
(79) The scanning electron microscopy (SEM) images were collected on a Quanta 400 FEG ESEM (FEI) at acceleration voltage of 0.2-30 kV. Infrared (IR) spectra were recorded on a Tensor 27FTIR spectrophotometer (Bruker). The X-ray powder diffraction (XRPD) measurements were performed with an X'Pert Pro MPD diffractometer (Panalytical) over a 28 range of 5 to 45. The thermogravimetric analysis (TGA) was performed on a Perkin-Elmer STA-600 under a constant flow of N.sub.2 at a temperature increase rate of 5 C./min. Zeta potential measurements were performed on a NanoZs Zetasizer from MALVERN whereas the Turbiscan measurements were performed with the MA 2000 (Formulaction, Toulouse, France). Gas adsorption isotherms for pressures in the range 0-120 kPa were measured by a volumetric approach using a Micrometrics ASAP 2420 instrument. All the samples were transferred to pre-dried and weighed analysis tubes and sealed with Transcal stoppers. Al-Fumarate and MIL-53 were evacuated and activated under dynamic vacuum at 10.sup.6 Torr at 140 C. for 8 hours. Ultra-high purity N.sub.2, CH.sub.4, H.sub.2 and CO.sub.2 gases were used for the experiments. N.sub.2 and H.sub.2 adsorption and desorption measurements were conducted at 77K. Surface area measurements were performed on N.sub.2 isotherms at 77K using the Brunauer-Emmer-Teller (BET) model with adsorption values increasing range of 0.005 to 0.2 relative pressures while the CH.sub.4 adsorption and CO.sub.2 adsorption measurements were done at 273 and 298 K, respectively.
Example 2Investigation into Changes in MOF Composition
(80) In order to investigate whether megasonics separation introduces changes in the MOF composition, -potential measurements were recorded after each washing step of Example 1 as shown Table 2.
(81) TABLE-US-00002 TABLE 2 - Potential of the Al-Fumarate and MIL-53 MOF material after each wash step using Megasonics using water as a dispersant. MOF washing process (Megasonics) - potential (mV) Al-Fumarate flow reactor +8.3 0.4 Al-Fumarate wash 1 in H.sub.2O +8.8 0.0 Al-Fumarate wash 2 in H.sub.2O +8.8 0.1 Al-Fumarate wash 3 in H.sub.2O +8.9 0.2 Al-Fumarate wash 4 in EtOH +10.6 0.2 Al-Fumarate wash 5 in EtOH +11.3 0.8 MIL-53 flow reactor +13.3 0.4 MIL-53 wash 1 in H.sub.2O +15.1 0.5 MIL-53 wash 2 in H.sub.2O +14.7 0.3 MIL-53 wash 3 in H.sub.2O +12.6 0.5 MIL-53 wash 4 in EtOH +12.7 0.2 MIL-53 wash 5 in EtOH +14.6 0.1
(82) No significant changes to the surface charge were observed, pointing to a separation that is based on reversible aggregation.
(83) To determine the quality of the crystals, XRPD and SEM measurements of the MOFs separated with megasonics and by the standard lab-scale centrifuge were compared. X-Ray powder diffraction (XRPD) confirmed the crystallinity of our Al-fum and MIL-53, showing identical patterns to those of crystals synthesized by solvothermal methods. It was observed by scanning electron microscope that the high-frequency treatment also does not affect the size and shape distribution of the MOFs.
(84) A comparison of the backscattering and transmission data of the supernatant collected from the first separation of the MOF containing solution using centrifuge and megasonics was undertaken as shown in
(85) The measurements of the BET surface areas revealed that the MOFs separated and washed with megasonics showed a drastic increase of 21% for the Al-Fum and 47% for MIL-53 over standard centrifuge washed MOF, which had BET values similar to literature (see Table 3 and
(86) TABLE-US-00003 TABLE 3 Comparisons of the reaction time between MOFs synthesized by convectional batch (using water as a reaction solvent) and by flow chemistry. BET surface areas, grams of MOF produced per 1 hour using flow chemistry and STY. Full adsorption isotherms are provided in the supplement information. STY Reaction Yield (Kg .Math. m.sup.3 .Math. SA.sub.BET time g h.sup.1 (%) d.sup.1) (m.sup.2 g.sup.1) From reactor Al-fum 1.2 min 338.04 109.0 25,040 MIL-53 1.2 min 50.68 112.8 3,754 Centrifuge x 5 Al-fum 1.2 min 281.88 90.9 20,880 890 MIL-53 1.2 min 42.14 93.8 3,121 806 Megasonics x 5 Al-fum 1.2 min 225.07 72.6 16,672 1075 MIL-53 1.2 min 35.10 78.1 2,600 1183 Commercial.sup.a Al-fum 10.2 min 174 86 5339 1140 Literature.sup.b MIL-53 4 hours 125 86 1300 1010 .sup.aM. Gaab, N. Trukhan, S. Maurer, R. Gummaraju and U. Mller, Microporous Mesoporous Mater., 2012, 157, 131-136. .sup.bP. A. Bayliss, I. A. Ibarra, E. Prez, S. Yang, C. C. Tang, M. Poliakoff and M. Schrder, Green Chem., 2014, 16, 3796.
(87) The Inventors attribute this improvement to the enhanced mass transfer that arises from acoustic streaming during megasonic application that promotes the removal of the excess organic ligands molecules inside of the pores. This is an important step forward for cost-effective and green production of MOFs as similar surface areas have only been obtained using laboratory scale methods that would be expensive at large scale, namely by using supercritical ethanol or calcination up to 330 C.
Example 3MOF Characterisation and Separation Parameters
(88) Megasonics Characterisation
(89) The separation of the MOFs was carried out in the experimental set up 200 shown in
(90) The power draw of the system 200 was determined using a standard power meter (not illustrated), although obtaining an accurate reading was difficult given the large fluctuations at each frequency. The average power draw of the system 200 at each frequency was determined over a 10 minute period of operation with a measurement taken at each minute interval from the power meter. At the completion of the 10 minute period the average power draw of the system at each frequency was determined. At frequencies of 1138, 860 and 578 kHz the power draw of the system was found to be 3997, 4222 and 40817 W, with the baseline power draw (whilst no ultrasonics were generated) of 84 W. This suggests the transducer's 210 power output for each of the frequencies (1138, 860 and 578 kHz) were 3157, 3382 and 32417 W.
(91) Separation Optimisation
(92) Several parameters were of interest when attempting to optimise the separation of the MOF; these included frequency, and reflector height.
(93) In order to determine the best frequency for MOF separation the megasonics vessel was first filled with 500 mL of clean (pre washed) Al-Fum and a frequency (1138, 860 or 578 kHz) was selected. Megasonics were then applied for a period of 10 minutes at 100% power and a reflector height of 14.5 cm, for the chosen frequency. At the end of the treatment period, the megasonics were switched off and the slurry allowed to freely settle for a period of 15 minutes. Following separation, the supernatant was decanted using a peristaltic pump and the volume was recorded before two solids samples were taken using the solids sampling valve 204 (
(94) Again the same Al-Fum MOF was left overnight before tests were undertaken to investigate the effect of reflector height. The vessel was filled to heights of 11.5, 14.5, 20.5 and 26.5 cm in succession, with megasonic treatment of 10 minutes at 100% and 1138 kHz. The MOF was once again allowed to settle for a period of 15 minutes before supernatant volume and bed mass fractions were taken in the same way as earlier described.
(95) Activation of MOF
(96) Following separation optimisation, transition was made from clean pre-washed MOF to reactor slurry in order to characterise the effects of the megasonics on both the activation process as well as any changes to the MOFs structure. In order to achieve this, 500 mL of Al-Fum reactor slurry was diluted to a 3 L batch. From this batch 500 mL was added to the megasonics vessel 202 and sonicated for 10 minutes at 100% power output with a frequency of 1138 kHz. At the conclusion of the treatment, the slurry was allowed to freely settle for 15 minutes before a solids sample was taken (8 mL) from the top layer (1 cm) of the bed. A peristaltic pump was then used to remove a total of 100 mL of supernatant. 100 mL of fresh water (milliQ grade) was added to the vessel prior to removal of the slurry from the megasonics vessel 202. The slurry was stirred briefly and a small sample (<5 mL) was taken for SEM analysis before being re-added to the vessel 202 for a further treatment. This was repeated until a total of 4 cycles (washes) had been completed. At the conclusion of the final washing stage, additional solids were removed for BET analysis.
(97) As a comparison, 500 mL of the same batch of diluted Al-Fum was centrifuged at 4500 RPM for 5 minutes. A small solids sample was taken for XRD analysis prior to the removal of 100 mL of supernatant. This was replaced with 100 mL of fresh water; the separated MOF was agitated before the process was repeated for a total of 4 washes. At the completion of 4 washes, additional solids were removed for the purpose of BET analysis
(98) Post reactor Mil-53 slurry was then used in place of Al-Fum and the same tests were repeated although in this case separation was achieved without initial the dilution (500 mL to 3 L) given its already dilute nature.
(99) Results and Discussion
(100) Optimal Frequency
(101) Carrying out treatments at each frequency, the greatest MOF separation (and hence greatest amount of separation) was achieved when treatment occurred with a frequency of 1138 kHz rather than 860 or 578 kHz (
(102) Effect of Reflector Height
(103) Various reflector heights (11.5, 14.5, 20.5 and 26.5 cm) were analysed for their effect on the degree of separation. Tests were carried out in this case at a frequency of 1138 kHz given that is was expected to be the most highly attenuating (lowest operable distance, Section 2.1.3) and was observed to give the highest degree of separation. From
(104) At greater reflector heights (20.5 cm and 26.5 cm), it was found that once again separation was reduced when compared to separation when using a reflector at 14.5 cm. This is undoubtedly due to acoustic attenuation which sees the amplitude of the sound die out at longer treatment distances. Although 14.5 cm was identified as the optimal reflector height, it did not lead to significant increases in the degree of separation and successful separations were carried out all heights (11.5 cm-26.5 cm).
(105) Activation of Metal-Organic Frameworks
(106) Comparing the effects of megasonic activation to centrifugation (Table 4), it is clear that significantly higher surface area has been achieved when megasonic treatment is applied. The measurements of the BET surface areas revealed that the MOFs separated and activated with megasonics showed an increase of 25% after 10 minutes (for the Al-Fum over standard centrifuge washed MOF, which had BET values similar to literature). We attribute this improvement to the enhanced mass transfer that arose from acoustic streaming during megasonic application promoting the removal of excess organic ligands molecules from the pores of the MOF crystals.
(107) TABLE-US-00004 TABLE 4 Water washing comparison, BET isotherms for centrifuge and megasonic Al-Fum washes at different times at 1138 kHz SA.sub.BET Methods (m.sup.2/g) Centrifuge 880 Megasonics 1 min 907 Megasonics 5 min 916 Megasonics 10 min 975 Megasonics 10 min in ETOH 1075
Example 4Continuous Megasonics Operation
(108) A prototype Continuous MOF separation process arrangement 300 according to the present invention was trialled as illustrated in
(109) In the process trial, a MOF containing solution with an initial temperature of 15 C. fed from feed flask 302 into the processing region 307 of the vessel 301. The transducer plate 312 was then operated to initially pre-sonicate the MOF containing solution for 10 min (100% nominal power with the 1 MHz transducer) prior to beginning flow operation, resulting in an increased temperature of the MOF containing solution of 20-25 C. After this pre-sonication step, flow was initiated by turning on the pumps 316, 317 and opening a drain valve 315A located at the bottom of the vessel 301. The input of MOF containing solution, along with an ice cooling bath 320 located on the sides of the processing region 307, enabled temperature to be maintained within an optimal range for efficient MOF separation and activation of between 20 and 40 C. across the entire process duration. The processed MOF was collected by removing the solution from the drain valve 315.
(110) Those skilled in the art will appreciate that the invention described herein is susceptible to variations and modifications other than those specifically described. It is understood that the invention includes all such variations and modifications which fall within the spirit and scope of the present invention.
(111) Where the terms comprise, comprises, comprised or comprising are used in this specification (including the claims) they are to be interpreted as specifying the presence of the stated features, integers, steps or components, but not precluding the presence of one or more other feature, integer, step, component or group thereof.