CATALYST AND PROCESS USING THE CATALYST FOR MANUFACTURING FLUORINATED HYDROCARBONS

Information

  • Patent Application
  • 20200086299
  • Publication Number
    20200086299
  • Date Filed
    September 07, 2017
    7 years ago
  • Date Published
    March 19, 2020
    4 years ago
Abstract
A catalyst comprising one or more metal oxides, wherein the catalyst has a total pore volume equal to or greater than 0.3 cm3/g and a mean pore diameter greater than or equal to 90 Å, where in the pore volume is measured using N2 adsorption porosimetry and the mean pore diameter is measured using N2 BET adsorption porosimetry.
Description

The invention relates to a catalyst, a method of preparing said catalyst and to a process that uses said catalyst. More particularly, the invention relates to a catalyst comprising one or more metal oxides and processes for using said catalyst in the addition or removal of halogen and halogen hydrides to/from compounds containing from 2 to 3 carbon atoms.


The listing or discussion of a prior published document in this specification should not necessarily be taken as an acknowledgement that the document is part of the state of the art or is common general knowledge.


Halocarbon-based compounds, particularly fluorocarbon-based compounds are currently used in a large number of commercial and industrial applications, such as propellants, blowing agents and heat transfer fluids. The interest in and use of fluorine-based compounds, particularly (hydro)fluoroolefins, as heat transfer fluids has increased as new refrigerants are sought.


(Hydro)haloalkenes such as hydrofluoropropenes can be conveniently prepared from corresponding hydro(halo)fluoroalkanes by dehydrohalogenation. The transformation can be effected thermally, i.e. by pyrolysis, catalytically, by contacting a hydro(halo)fluoroalkane with a catalyst under suitable conditions, or chemically, typically by contacting a hydro(halo)fluoroalkane with strong bases such as alkali metal hydroxides. For commercial operation, catalytic dehydrohalogenation is believed to be preferred.


The hydrofluoropropene 1,1,1,2,3-pentafluoropropene (HFO-1225ye), for example, can be prepared by contacting and dehydrofluorinating 1,1,1,2,3,3-hexafluoropropane in the gaseous state with trivalent chromium oxide or partially fluorinated trivalent chromium oxide, optionally in the presence of oxygen (see U.S. Pat. No. 5,679,875).


Similarly, fluorination and/or hydrofluorination steps are also common in the manufacturing processes of (hydro)fluoroalkenes. Such processes may be performed by contacting HF with one or more (hydro)haloalkenes or (hydro)haloalkanes, preferably in the presence of a catalyst.


Notwithstanding the above processes, catalytic reactions involving halocarbons have a number of problems in use, one of which is that industrial scale processes subject the catalysts to extreme temperatures and pressures, numerous regenerations and corrosive reagents. The skilled person will know that over the lifetime of an industrial catalyst the activity is steadily reduced and the catalyst must eventually be replaced in an expensive procedure.


There is therefore a need for catalysts with improved stability and comparable or improved activity relative to existing catalysts.


In a first aspect, the present invention provides a catalyst comprising one or more metal oxides and wherein the catalyst has a total pore volume of greater than 0.3 cm3/g and the mean pore diameter is greater than or equal to 90 Å, wherein the total pore volume is measured by N2 adsorption porosimetry and the mean pore diameter is measured by N2 BET adsorption porosimetry.


The skilled person would appreciate that in catalysis in general, catalytic activity is understood to be proportional to the available surface area of the catalyst. It is to be expected that increasing the opportunity for the reagents to interact with the surface of the catalyst will improve the rate of conversion.


However, in contrast to established teaching, the present inventors have surprisingly found that increasing the pore volume and average pore diameter, which may inherently reduce a catalyst's surface area, increases both the stability and the activity of the catalyst.


Without wishing to be bound by theory, it is believed that this is a result of the increased mass transfer through the catalyst and that this effect is more pronounced for C3 compounds than C2 compounds. Also without wishing to be bound by theory, it is believed that the wider pore diameters of the present invention allow the catalyst in use to assume more quickly an effective pore structure for producing (hydro)haloalkenes such as hydrofluoropropenes.


The pore structure of solid porous materials can be determined by several methods, one of the most commonly used is the adsorption and desorption of N2, based on the BET theory (Brunauer, Emmett and Teller) of the adsorption of multilayers of condensed gases onto solid surfaces, and the evaporation (desorption) of the adsorbed gas during desorption. Nitrogen is a common adsorbate for probing the micro and mesoporous regions. From the adsorption and desorption isotherms, the following can be calculated:


BET surface area from the adsorption of a monolayer of N2, total pore volume taken from the amount of nitrogen adsorbed at P/P°=0.99 and average pore diameters can be determined using different calculations either based on the BET theory or that of BJH (Barrett, Joyner and Halenda), either from the adsorption or desorption data.


Preferably, the total pore volume of the catalyst is equal to or greater than 0.35 cm3/g or 0.4 cm3/g, such as 0.45 cm3/g, 0.5 cm3/g, 0.55 cm3/g or even 0.6 cm3/g when measured by N2 adsorption porosimetry.


Preferably, the average pore width of the catalyst is greater than or equal to 100 Å, e.g. greater than or equal to 110 Å or greater than or equal to 120 Å when measured by N2 BET adsorption porosimetry.


Preferably, the average pore width of the catalyst is greater than or equal to 130 Å, e.g. greater than or equal to 140 Å, greater than or equal to 150 Å or greater than or equal to 170 Å when measured by N2 BJH adsorption porosimetry.


Preferably, the average pore width of the catalyst is greater than or equal to 90 Å, e.g. greater than or equal to 100 Å, greater than or equal to 110 Å or greater than or equal to 120 Å when measured by N2 BJH desorption porosimetry.


Preferably, the catalyst is provided in the form of a pellet or pellets comprising a plurality of catalyst particles. Such catalyst particles may be pressed together, for example under load, to form the pellets.


The pellets may comprise one or more further materials. For example, the pellets may include graphite, preferably in an amount of from about 0.5 wt % to about 10 wt %, e.g. from about 1 wt % to about 5 wt %.


Preferably, the pellets have a longest dimension from about 1 mm to about 100 mm. In some embodiments, the pellets may have a longest dimension of about 1 mm to about 10 mm, for example from about 3 mm to about 5 mm.


The catalyst may be supported or unsupported. Typically, the metal in the metal oxide catalyst is one or more of any metal which forms a metal (oxy)fluoride which has Lewis acid character. Examples are metals selected from Li, Na, K, Ca, Mg, Cs, Al, Sc, Y, Ti, Zr, Hf, V, Nb, Ta, Cr, Mo, W, Mn, Re, Fe, Ru, Co, Rh, Ir, Ni, Pd, Pt, Cu, Ag, Au, Zn, La and Ce. Preferably, the metal is a transition metal and even more preferably is chromium.


The metal oxide catalyst used in the process of the invention may contain at least one additional metal or compound thereof. This additional metal or compound thereof can also be referred to as a promoter. In one embodiment, at least one additional metal is selected from Li, Na, K, Ca, Mg, Cs, Sc, Al, Y, Ti, Zr, Hf, V, Nb, Ta, Cr, Mo, W, Mn, Re, Fe, Ru, Co, Rh, Ir, Ni, Pd, Pt, Cu, Ag, Au, Zn, La, Ce and mixtures thereof. Preferably, the at least one additional metal is selected from Li, Na, K, Ca, Mg, Cs, Cr, Zr, Nb, Pd, Ta, Zn, V, Mo, Ni, Co and mixtures thereof, even more preferably the additional metal is zinc.


Advantageously, the catalyst may be a zinc/chromia catalyst. By the term “zinc/chromia catalyst” we mean that the metal oxide catalyst comprises chromium or a compound of chromium and zinc or a compound of zinc.


The total amount of the zinc or a compound of zinc present in the zinc/chromia catalysts of the invention is typically from about 0.01 wt % to about 25 wt %, preferably 0.1 wt % to about 25 wt %, conveniently 0.01 wt % to 6 wt % zinc, and in some embodiments preferably 0.5% by weight to about 25% by weight of the catalyst, preferably from about 1 to 10% by weight of the catalyst, more preferably from about 2 to 8% by weight of the catalyst, for example about 4 to 6% by weight of the catalyst.


Preferably, the catalyst comprises at least 80 wt % (for example at least 85 wt %, at least 90 wt %, at least 92 wt %, at least 93 wt %, at least 94 wt %, at least 95 wt % or at least 96 wt %) chromia.


In some embodiments, the catalyst may be in fluorinated form. For example, the catalyst may have been fluorinated by treatment with HF at elevated temperature.


Advantageously, the catalysts of the present invention are unused, i.e. new. By ‘unused’ we mean that the catalyst possesses the total pore volume and average pore diameter, as specified above, before it has been contacted with any reagents or put under any pre-reaction conditions and/or the catalyst has not previously been used for catalysing a reaction or regenerated.


The present invention also provides a method of preparing a catalyst, said method comprising the steps of:

    • a) preparing a metal salt solution and a hydroxide solution;
    • b) combining the solutions at a pH of greater than 7.5 in order to precipitate the metal hydroxide(s);
    • c) drying the precipitated metal hydroxides;
    • d) calcining the metal hydroxide(s) to form the metal oxide(s).


Preferably, the metal salt comprises a nitrate salt such as a hydroxide nitrate salt. In preferred embodiments, the metal salt comprises chromium, and may comprise a chromium nitrate salt such as Cr(OH)(NO3)2. The hydroxide solution may comprise ammonium hydroxide (NH4OH). Advantageously, step b) is carried out at a pH of greater than 8. Preferably, step b) is carried out at a pH of greater than or equal to 8.1, 8.2, 8.3; 8.4 or 8.5.


In some embodiments, the metal salt solution is provided at a concentration of from about 1 mol/l to about 10 mol/l, for example from about 2 mol/l to about 8 mol/l, e.g. from about 3 mol/l to about 7 mol/l or from about 4 mol/l to about 6 mol/l.


In some embodiments, the hydroxide solution is provided at a concentration of from 1 mol/1 to about 10 mol/l, for example from about 2 mol/l to about 8 mol/l, e.g. from about 3 mol/1 to about 7 mol/l or from about 4 mol/l to about 6 mol/l.


Preferably, step (b) is performed by combining the solutions in a body of solvent, such as water. Alternative solvents may include alcohols, glycols, water mixtures and other polar solvents.


Preferably, step b) is carried out at a substantially constant temperature, such as from 0 to 50° C., preferably from 10 to 30° C.


Preferably, step (b) is performed while agitating the combined solutions. Such agitation may be provided by known suitable means such as impellers, jet mixer, recirculation pumps and the like.


The precipitate formed during step (b) preferably comprises particles having average longest dimensions of from about 5 μm to about 20 μm, e.g. from about 7 μm to about 15 μm or from about 8 μm to about 13 μm, for example around 10 μm. Such dimensions are according to measurement by focussed beam reflectance measurement.


Preferably, step (c) includes removing liquid from the slurry of metal hydroxide precipitate(s) to produce a wet cake, for example by filtration or centrifugal action. Such filtration may include the application of a pressure differential across the or a filtration membrane. The cake may be washed prior to any drying or calcining, preferably by exposure to water (e.g. deionised water) or aqueous alkali (such as ammonium hydroxide).


Preferably step (c) includes removing liquid, e.g. residual liquid, from the wet metal hydroxide(s) cake by exposing it to elevated temperature. Such elevated temperature may be, for example, between 50° C. and 200° C. and more preferably may be between 80° C. and 150° C., e.g. around 90° C. to around 120° C. The precipitate is preferably exposed to the elevated temperature for at least 15 mins, e.g. at least 30 mins or at least 1 hr. In certain embodiments, the precipitate may be subject to elevated temperature for over 6 hr or over 12 hr.


It is also preferred that step (d) includes a step of calcining the metal hydroxide, preferably after liquid removal and/or drying. Such a calcining step may include heating the metal hydroxides to a temperature between around 200° C. and around 550° C., for example between around 250° C. and around 500° C., e.g. around 300° C. to around 400° C. Such a calcining step may have a duration of from around 5 mins to around 12 hrs. It is particularly preferred to perform the calcination for a sufficient period to produce a catalyst having a TGA loss on ignition (LOI) of less than around 15%, for example less than around 12% or less than around 10%, for example around 8%, when heating to 400° C.


The method preferably comprises combining the calcined metal oxide with graphite to provide a catalyst composition comprising around 0.1 wt % to around 10 wt % graphite. In preferred embodiments, the composition so formed may comprise around 0.5 wt % to around 5 wt % graphite. It is most preferred that the composition so formed comprises around 1 wt′)/0 to around 3 wt % graphite.


In preferred embodiments, the metal oxide and/or catalyst composition may be pressed to form catalyst pellets. The pressing may take place under a load of around 1 to 10 tonnes, e.g. around 5 tonnes. The pellets so formed may have a longest dimension from about 1 mm to about 100 mm. In some embodiments, the pellets may have a longest dimension of about 1 mm to about 10 mm, for example from about 3 mm to about 5 mm.


In embodiment further aspect of the invention, there is provided a process for fluorinating a C2-3 hydrohalocarbon species, comprising contacting the species with a catalyst according to the invention. This is typically carried out in the presence of HF. For the avoidance of doubt, the term C2-3 hydrohalocarbon includes saturated or unsaturated compounds with a two or three carbon chain and containing one or more atoms of hydrogen and a halogen (F, Cl, Br, I). In preferred embodiments, the hydrohalocarbon species comprises a C3 hydrohalocarbon species.


An example of such a process comprises contacting trichloroethylene with the catalyst in the presence of HF to produce 1,1,1,2-tetrafluoroethane (134a), the conversion of 1,1,1,2,3-pentachloropropane (240db) to 2-chloro-3,3,3-trifluoropropene (1233xf), the conversion of 1233xf to 2,3,3,3-tetrafluoropropene (1234yf) and/or 1,1,1,2,2-pentfluoropropane (245cb), the conversion of 1,1,1,3-tetrachloropropane (250fb) to 3,3,3-trifluoropropene (1243zf), or the conversion of 2,3-dichloro-1,1,1-trifluoropropane (243db) to 1233xf and/or 1234yf.


In another aspect of the invention, there is provided a process for dehydrohalogenating a 02-3 hydrohalocarbon species (preferably a C3 hydrohalocarbon species), comprising contacting the species with a catalyst, such as contacting a hydro(halo)fluoropropane with the catalyst to produce a fluoropropene, preferably a tetrafluoropropene (1234) such as 1234ze ((E) or (Z)) or 1234yf. Advantageously, this may include the conversion of 245cb and/or 1,1,1,2,3-pentafluoropropane (245eb) to 2,3,3,3-tetrafluoropropene (1234yf) and/or 1,3,3,3-tetrafluoropropene (1234ze), the conversion of 1,1,1,3,3-pentafluoropropane (245fa) to 1234ze or the conversion of 1-chloro-1,3,3,3-tetrafluoropropane to 1-chloro-3,3,3-trifluoropropene (1233zd) or 1234ze.


In a further aspect of the invention, there is provided a process for eliminating HF or from a saturated C2-3 hydrohalocarbon species (preferably a C3 hydrohalocarbon species), comprising contacting the species with a catalyst according to the invention.


In a further aspect of the invention, there is provided a process for adding HF to an unsaturated C2-3 hydrohalocarbon species (preferably a C3 hydrohalocarbon species), comprising contacting the species with a catalyst according to the invention.


The claimed processes may be conducted in the liquid or the vapour phase but are preferably conducted in the vapour phase. The process may be carried out at atmospheric, sub- or super atmospheric pressure, typically at from 0 to about 30 bara, preferably from about 1 to about 20 bara, such as 15 bara.


Typically, the vapour phase process of the invention is carried out a temperature of from about 100° C. to about 500° C. (e.g. from about 150° C. to about 500° C. or about 100 to about 450° C.). Preferably, the process is conducted at a temperature of from about 150° C. to about 450° C., such as from about 150° C. to about 400° C., e.g. from about 175° C. to about 300° C. Lower temperatures may also be used in the conversion of 250fb to 1243zf, such as from about 150° C. to about 350° C., e.g. from about 150° C. to about 300° C. or from about 150° C. to about 250° C.


The processes typically employ a molar ratio of HF:organics of from about 1:1 to about 100:1, such as from about 3:1 to about 50:1, e.g. from about 4:1 to about 30:1 or about 5:1 or 6:1 to about 20:1 or 30:1.


The reaction time for the process generally is from about 1 second to about 100 hours, preferably from about 10 seconds to about 50 hours, such as from about 1 minute to about 10 or 20 hours. In a continuous process, typical contact times of the catalyst with the reagents are from about 1 to about 1000 seconds, such from about 1 to about 500 seconds or about 1 to about 300 seconds or about 1 to about 50, 100 or 200 seconds.





The present invention will now be illustrated by the following non-limiting Examples, illustrated by the following drawings:



FIG. 1 shows a plot of the particle size distribution at temporal points during the reaction of Comparative Example 8, unweighted to emphasise smaller particles;



FIG. 2 shows a plot of the particle size distribution at temporal points during the reaction of Comparative Example 8, weighted to emphasise larger particles;



FIG. 3 shows a plot of the particle size distribution at temporal points during the reaction of Example 9, unweighted to emphasise smaller particles;



FIG. 4 shows a plot of the particle size distribution at temporal points during the reaction of Example 9, weighted to emphasise larger particles;



FIG. 5 shows a plot of the particle size distribution at temporal points during the reaction of Comparative Example 10, unweighted to emphasise smaller particles;



FIG. 6 shows a plot of the particle size distribution at temporal points during the reaction of Comparative Example 10, weighted to emphasise larger particles;



FIG. 7 shows a plot of the particle size distribution at temporal points during the reaction of Example 11, unweighted to emphasise smaller particles;



FIG. 8 shows a plot of the particle size distribution at temporal points during the reaction of Example 11, weighted to emphasise larger particles;



FIG. 9 shows a plot of the presence of fine particles during the reactions of Examples and Comparative Examples 8 to 11;



FIG. 10 shows a plot of the particle size distributions at completion of the reactions of Examples and Comparative Examples 8 to 11 unweighted to emphasise smaller particles;



FIG. 11 shows a plot of the particle size distributions at completion of the reactions of Examples and Comparative Examples 8 to 11 weighted to emphasise larger particles.





EXAMPLES

Catalysts of examples 1 to 7 were produced by the following method:


500 mL deionised water heel was added to a 1.7 L jacketed glass vessel, fitted with an overflow, overhead stirrer, pH probe and thermocouple and cooled to 15° C. The stirrer was actuated at 500 rpm, save for in example 5, where it was turned at 250 rpm.


Zn(NO3)2.6H2O (19.03 g) was dissolved into a solution of Cr(NO3)2(OH)(aq) (500 g) in a 600 mL beaker. In another beaker, 500 g 17% NH4OH solution was provided.


The metal and ammonia solutions were pumped into the chilled water at 5 ml/min.


Precipitation of a green/blue solid occurs immediately. The pH of the mixture was monitored and the reactant flow rates adjusted to maintain the target pH for each example as shown in Table 1, below. The reaction was run until all of the metal solution was added.


The slurry was filtered under vacuum until a filter cake formed then washed four times with de-ionised water (“a” examples) or dilute aqueous ammonia solution (“b” examples).


The filter cake was then dried at 105° C. overnight in a standard oven, followed by calcining under flowing nitrogen (200 ml/min) at 300° C. for 12 hours to produce 6.5% ZnO/Cr2O3, the heating rate on the chamber furnace being set to 2° C./min. The percentage mass loss was on calcination was noted.


2 wt % graphite was blended with the cooled, calcined catalyst precursor in a waring blender, and the resultant mixture was sieved to <250 μm. The sieved mixture was formed into pellets under a load of 5 tonne in a 32 mm pellet die, 3 g per pellet.


The pellets were then ground to mesh size 0.5-1.4 mm for catalyst testing. Surface area, pore volumes and sizes were measured by N2 adsorption/desorption porosimetry. Zn content was measured by X-ray fluorescence spectroscopy. The results are shown in Table 1, alongside results for Comparative Example 1, a chromia catalyst having a specified surface area of 160 to 200 m2/g and pore volume of greater than 0.22 cm3/g.










TABLE 1








N2 Porosimetry



(200-500 μm, outgassed 300° C., 3 h, N2)
























Pore Volume
BET Ads
BJH Ads
BJH Des



Actual
Water
Stirrer


BET SA
(cm3/g) @
Average pore
Average pore
Average pore


Example
pH
Heel/g
speed/rpm
Temp/° C.
Slurry Wash Soln
(m2/g)
0.99P/P°
width (Å)
width (Å)
width (Å)




















CE1





180
0.282
63
107
65


CE2a
7.2-7.3
500
500
15-17
DI H2O
171
0.259
60
112
63


CE2b




NH4OH
125
0.221
71
124
72


3a
7.5-8.1
500
500
15-16
DI H2O
125
0.327
105
147
102


3b




NH4OH
127
0.382
121
169
116


4
8.3
500
500
15-16
DI H2O
129
0.442
137
184
129


5a
8.3-8.4
500
500
17-18
DI H2O
111
0.449
162
190
143


5b




NH4OH
111
0.464
167
195
147


6a
8.3-8.4
500
500
15-16
DI H2O
172
0.506
118
192
127


6b




NH4OH
138
0.447
129
189
131


7a
8.2-8.4
500
500
15-17
DI H2O
132
0.512
155
198
148


7b




NH4OH
151
0.508
135
191
138









The data clearly shows that a significant raising of the pore volume of a precipitated catalyst is provided when the pH of precipitation is raised.


The pelleted catalysts were tested for their efficacy in converting trichloroethylene to 134a. An atmospheric pressure screening rig was equipped with four reactor tubes, each with independent HF, organic and nitrogen feeds. The organic feed system was charged with trichloroethylene. Each reactor was charged with 2 g of catalyst with a particle size in the range 0.5-1.4 mm. Initially the nitrogen flow (60 ml/min) was directed to the reactor inlet and the catalysts dried at 250° C. for 1 hour.


Following the catalyst drying operation HF vapour was fed to each reactor at a flow of 30 ml/min, diluted with nitrogen (60 ml/min), and passed over the catalysts at 250° C. for approximately 30 minutes until HF was observed in the reactor off gases. At this point the nitrogen flows (reduced to 30 ml/min) were redirected to the reactor exits. The catalysts were then exposed to the HF:N2 (30:5-ml/min) stream for a further hour at 250° C. before the temperatures were ramped to 450° C. at 40° C. per hour. These temperatures were held for ten hours.


The reactors were initially cooled to 350° C. and trichloroethylene was fed over the catalysts by sparging nitrogen (8 ml/min) through liquid trichloroethylene at 10° C. This gave a 0.5 ml/min flow of trichloroethylene gas. The catalysts were allowed to equilibrate in the HF:trichloroethylene:N2 (30:0.5:10-ml/min) gas stream for about 2 hours before the reactor temperatures were reduced to 300° C. The catalysts were again allowed to equilibrate for about 1 hour before the production of 133a and 134a from each was measured. The temperatures and yields across the reactors were monitored.


The organic feed was then turned off and with 30 ml/min HF flowing over the catalyst the reactor temperatures were ramped to 490° C. at 40° C./hr this was held for ten hours and cooled to 350° C. Trichloroethylene was then provided as above. This process was repeated for a stress temperature of 514° C. and, for some examples 522° C.


The activity and stability results are presented as a comparison to the results for Comparative Example 1, a commercial catalyst tested under the same conditions.


Activity is determined according to the calculation





Activity=50(S2−RT)


where S2 is the predicted reaction temperature to obtain 10% 134a yield at Stress Temperature 2 and where RT is 287.5° C.


Stability is determined according to the calculation





Stability=50−(S3−RT)


where S3 is the predicted reaction temperature to obtain 10% 134a yield at Stress Temperature 3 and where RT is 287.5° C.


The results are shown in Table 2, below.












TABLE 2









Predicted Reaction Temp to Obtain




Precip-
10% 134a Yield















Exam-
itation
Stress 1
Stress 2
Stress 3
Stress 4
Ac-



ple
pH
450° C.
490° C.
514° C.
522° C.
tivity
Stability

















CE 1

288.90
287.50
295.50
318.90
50
42


CE2a
7.2-7.3
296.00
297.04
308.61

40.5
28.9


CE2b

307.64
292.58
301.11

44.9
36.4


3a
7.5-8.1
287.22
284.37
291.35

53.1
46.2


3b


279.71
281.90

57.8
55.6


4
8.3
284.70
286.04
284.79
304.00
51.5
52.7


5a
8.3-8.4
288.46
286.80
290.93
308.82
50.7
46.6


5b

286.78
284.96
289.00
308.18
52.5
48.5


6a
8.3-8.4
282.16
279.32
283.17
301.29
58.2
54.3


6b

281.68
285.05
288.90
306.29
52.5
48.6


7a
8.2-8.4
281.48
282.46
288.26
303.83
55.0
49.2


7b

282.35
278.32
282.84
297.90
59.2
54.7









The results show a clear correlation between increased pore volume and width and increased stability and activity over prior art catalysts. This activity appears to be sustained even where there is a decrease in surface area compared to the commercial catalyst.


Examples 8 and 9 and Comparative Examples 10 and 11

Catalysts were prepared substantially according to the method of Examples 1 to 7, adapted as described below with reference to Table 3.


A Mettler Toledo Optimax automated laboratory reactor was fitted with Focussed Beam Reflective Measurement (FBRM) G400 14 mm probe with overhead stirring and charged with 500 ml a deionised water heel.


The metal solution was pumped to the reactor at 5 ml/min. 17% Ammonium hydroxide solution was also added at 5 ml/min. The pH was closely monitored and the flow rates of the reactants altered to maintain the target pH. The reaction was run until 300 g of the metal solution was added. The particle size of the precipitate was monitored during the reaction using the FBRM G400 probe.











TABLE 3







Target


Example
Metal solution
pH







CE8
300 g Chromium hydroxide nitrate (~10% Cr)
pH 7


 9
300 g Chromium hydroxide nitrate (~10% Cr)
pH 8.5


CE10
300 g Chromium hydroxide nitrate (~10% Cr) +
pH 7



11.4 g Zn(NO3)2•6H2O


11
300 g Chromium hydroxide nitrate (~10% Cr) +
pH 8.5



11.4 g Zn(NO3)2•6H2O









The resulting slurries were vacuum filtered and washed three times with de-ionised water. The filter cake was dried at 110° C. then, calcined under flowing nitrogen (200 ml/min) at 300° C. for 12 hours to produce Cr2O3 and 6.5% ZnO/Cr2O3. This was milled and mixed with 2% graphite before being pelleted at 5 tonne.


Comparative Example 8


FIGS. 1 and 2 and table 4 show the measured particle size distribution 2, 6 and 15 minutes after the start of dosing and once dosing is complete. 2 minutes after the start there are mostly very small particles, but also a few large particles present. These large particles are not present 6 minutes after the start of dosing, by which time the small particle population is at its greatest. Thereafter, the distribution shows a gradual shift to large size.













TABLE 4





Statistic
2 min.
6 min.
15 min.
End



















Median No Wt
3.7
4.3
6.2
8.7


Mean Sq Wt
67.8
12.6
16.6
24.4


Counts <5 μm
45949
66179
42031
21046


Counts 5-8 μm
12838
25269
27048
19349


Counts 8-25 μm
10920
22241
37550
42532


Counts 25-300 μm
1493
357
1576
5377









Example 9


FIGS. 3 and 4 and table 5 show the measured particle size distribution 2, 6 and 15 minutes after the start of dosing and once dosing is complete. 2 minutes after the start there are mostly large particles present. But by 6 minutes, the number of large particles has reduced, and the number of small particles has increased significantly. The particle system shows very little change for the final 15 minutes of dosing.















TABLE 5







Statistic
2 min.
6 min.
15 min.
End






















Median No Wt
8.6
4.3
4.0
3.9



Mean Sq Wt
30.1
13.4
11.8
11.5



Counts <5
10732
60239
77458
81366



Counts 5-8
7135
22430
26103
26522



Counts 8-25
16259
21560
20603
20341



Counts 25-300
3858
460
233
228










Comparative Example 10


FIGS. 5 and 6 and table 6 show the measured particle size distribution 2, 6 and 15 minutes after the start of dosing and once dosing is complete. 2 minutes after the start there are mostly small particles present which increase in number as 6 minutes is reached. After that, the population of those small particles gradually decreases, and the number of larger particles increases.













TABLE 6





Statistic
2 min.
6 min.
15 min.
End



















Median No Wt
5.9
5.3
6.8
7.3


Mean Sq Wt
19.7
17.0
23.4
26.7


Counts <5 μm
29859
46790
32806
28764


Counts 5-8 μm
15510
22717
20755
19240


Counts 8-25 μm
23382
28384
35207
35337


Counts 25-300 μm
1798
1346
4113
5314









Example 11


FIGS. 7 and 8 and table 7 show the measured particle size distribution 2, 6 and 15 minutes after the start of dosing and once dosing is complete. The distributions show that over the course of dosing, there is a gradual increase in the numbers of smaller particles. For the final 15 minutes of dosing, there is a decrease in the number of larger particles.













TABLE 7





Statistic
2 min.
6 min.
15 min.
End



















Median No Wt
5.7
4.3
4.1
3.6


Mean Sq Wt
16.8
13.2
12.4
10.4


Counts <5 μm
12933
52574
61877
87005


Counts 5-8 μm
7197
19203
21662
24208


Counts 8-25 μm
9559
17822
19193
16282


Counts 25-300 μm
352
297
284
112










FIG. 9 shows the real time data collection for the fines count (less than 5 μm and 8 μm to 25 μm) for Comparative Examples 8 and Example 9. From this it was possible to see instantly the effect of any flow disturbances or pH fluctuations. It also demonstrates that leaving the final slurry to stir for an extended period had no effect on particle size or distribution.


A comparison of the final particle size distributions of the slurries is shown in FIGS. 10 and 11 and Table 8. The results clearly show that increasing the pH of precipitation has a significant effect on the particle population and size. Both runs at pH 8.5 have a smaller average size than those at pH 7.0, and more small particles. Changing the metal composition also has an effect but much smaller in scale. Both runs with zinc show a slightly smaller average size compared to the chromium only counterparts.


The resulting dried, calcined and pelleted catalysts were tested by N2 adsorption/desorption porosimetry to determine surface area, total pore volume and average pore diameter. The results are shown in Table 8, below.














TABLE 8









Pore





Mean particle

volume
BJH Ads




length (slurry)
BET
cm3/g
Average pore


Example
pH
Microns
m2/g
@P/P°0.99
diameter Å




















CE8
7
24.5
243.75
0.21
51.2


 9
8.5
11.4
207.69
0.64
189.2


CE10
7
26.5
241.00
0.45
100.1


11
8.5
10.5
200.98
0.72
206.7









It is clear that the catalysts of Comparative Examples 8 and 10 (prepared at pH 7) had a larger particle size in the slurry and a larger BET surface area and a smaller pore diameter and volume. In contrast, the catalysts of Examples 9 and 11 (prepared at pH 8.5) had a smaller particle size in the slurry which resulted in a smaller BET surface area and a larger pore diameter and volume.


The catalysts of Examples 9 and 11 and Comparative Examples 8 and 10 were subjected to the same performance testing as Examples 1 to 7. The results are shown in Table 9 below.











TABLE 9









Predicted temp to



Obtain 10% 134a Yield















Stress 1
Stress 2
Stress 3


Example
Activity
Stability
450° C.
490° C.
514° C.















CE8
42.4
34.33
285.03
295.10
303.17


 9
50.27
48.38
287.36
287.23
289.12


CE10
45.89
46.93
295.66
291.61
290.57


11
59.08
46.27
274.38
278.42
291.23









These results show improved stability of the catalysts of Examples 9 and 11 over the comparative Examples 8 and 10. This demonstrates that the favouring of larger pore sizes, larger pore volumes and/or smaller precipitated particle diameter upon precipitation over BET surface area provides for improved performance in the catalysts. These parameters may be controlled by controlling the pH of precipitation.


Preferences and options for a given aspect, feature or parameter of the invention should, unless the context indicates otherwise, be regarded as having been disclosed in combination with any and all preferences and options for all other aspects, features and parameters of the invention.


Example 12 and Comparative Example 13

In Example 12, chromia catalyst pellets were made according to the following method. 500 mL deionised water heel was added to a 1.7 L jacketed glass vessel, fitted with an overflow, overhead stirrer, pH probe and thermocouple and cooled to 15° C. The stirrer was actuated at 500 rpm


A solution of Cr(NO3)2(OH)(aq) (1036 g) was measured into a 2000 mL beaker. In another beaker, 599 g 17% NH4OH solution was provided.


The metal and ammonia solutions were pumped into the chilled water at 5 ml/min. Precipitation of a green/blue solid occurs immediately. The pH of the mixture was monitored and the reactant flow rates adjusted to maintain the target of pH 8.5. The reaction was run until all of the metal solution was added.


The chromium hydroxide slurry was divided into two portions and filtered separately under vacuum until a filter cake formed then each washed three times with de-ionised water (3×500 mL). The resulting filter cakes were combined, then divided into four. One portion of cake was then dried at 80° C. for 3-days in a standard oven, followed by calcining under flowing nitrogen (200 ml/min) at 300° C. for 12 hours to produce Cr2O3, the heating rate on the chamber furnace being set to 2° C./min. The percentage mass loss was on calcination was noted.


2 wt % graphite was blended with the cooled, calcined catalyst precursor in a waring blender, and the resultant mixture was sieved to <250 μm. The sieved mixture was formed into pellets under a load of 5 tonne in a 32 mm pellet die, 3 g per pellet.


The pellets were then ground to mesh size 0.5-1.4 mm for catalyst testing. Surface area, pore volumes and sizes were measured by N2 adsorption/desorption porosimetry.


Production of 1234yf from 243db


The performance of the catalyst of Example 12 was tested for the production of 1234yf from the fluorination of 243db by contact with HF and compared to the performance for a commercially available chromia catalyst containing no promoter. The pore volumes and diameters for each catalyst were also tested.


An atmospheric pressure screening rig was equipped with four reactor tubes, each with independent HF, organic and nitrogen feeds. The organic feed system was charged with 243db. Each reactor was charged with 2 ml of catalyst with a particle size in the range 0.5


1.4 mm. Initially the nitrogen flow (60 ml/min) was directed to the reactor inlet and the catalysts dried at 200° C. for 2 h.


Following the catalyst drying operation HF vapour was fed to each reactor at a flow of 30 ml/min, diluted with nitrogen (60 ml/min), and passed over the catalysts at 300° C. for approximately 60 minutes until HF was observed in the reactor off gases. At this point the nitrogen flows (reduced to 30 ml/min) were redirected to the reactor exits. The reactor temperatures were ramped to 360° C. at 40° C. per hour. These temperatures were held for ten hours.


The reactors were cooled to 350° C. and 243db was fed over the catalysts by sparging nitrogen (4-6 ml/min) through liquid 243db at 10° C. This gave a 0.5-1 ml/min flow of 243db gas. The catalysts were allowed to equilibrate in the HF:243db:N2 (30:0.5-1.0:4-6 ml/min) gas stream for about 1 h before sampling reactor off-gas into a glass burette with DI water for GC analysis. The results are shown in Table 10 below.

















TABLE 10










Pore volume








243db
1243yf
pre test (N2








conversion
selectivity
absorption)/
Pore volume post test
Average BJH ads pore
Average BJH ads pore


Example
Catalyst
Temperature/° C.
%
%
cm3/g
(N2 absorption)/cm3/g
diameter pre test/Å
diameter post test/Å







12
Cr2O3
350
100
40.26
0.44
0.34
147
261


CE13
Cr2O3
350
100
17.95
0.28
0.21
101
167









The results show a clear improvement in selectivity for 1234yf when the catalyst of the present invention is utilised. Furthermore, the results show that the catalyst of the invention shows significant pore widening once used, which without wishing to be bound by any theory, may amplify the effect of providing a high pore volume and average pore diameter in the unused catalyst.


Example 14

500 mL deionised water heel was added to a 1.7 L jacketed glass vessel, fitted with an overflow, overhead stirrer, pH probe and thermocouple and cooled to 15° C. The stirrer was actuated at 430 rpm. A solution of Cr(NO3)2(OH)(aq) (332 g) was measured into a 600 mL beaker and 17% NH4OH solution (476 g) into another beaker.


The metal and ammonia solutions were pumped into the chilled water at 5 ml/min. Precipitation of a green/blue solid occurs immediately. The pH of the mixture was monitored and the reactant flow rates adjusted to maintain the target pH 8.5. The reaction was run until all of the solutions were added.


The chromium hydroxide slurry was filtered under vacuum until a filter cake formed then washed with de-ionised water (3×500 mL). The filter cake was then dried at 105° C. overnight in a standard oven, followed by calcining under flowing nitrogen (200 ml/min) at 300° C. for 12 hours to produce Cr2O3, the heating rate on the chamber furnace being set to 2° C./min.


2 wt % graphite was blended with the cooled, calcined catalyst precursor in a waring blender, and the resultant mixture was sieved to <250 μm. The sieved mixture was formed into pellets under a load of 5 tonne in a 32 mm pellet die, 3 g per pellet. The pellets were then ground to mesh size 0.5-1.4 mm for catalyst testing.


Analysis showed a BET surface area of 211 m2/g, a Pore Volume @0.99P/P° of 0.731 cm3/g and average BJH adsorption pore diameter of 199 Å.


Example 15

A further catalyst was produced according to the method of Examples 1 to 7, targeting a pH of 8 to 8.5 during production.


Production of 1234yf and 245cb from 1233xf


The performance of the catalyst of Examples 12, 14 and 15 was tested for the production of 1234yf and 245cb from the fluorination of 1233xf by contact with HF. The results were compared to those of a commercially available chromia catalyst (Comparative Example 16).


Each catalyst (3 mL, 0.5-1.4 mm) was charged to an 0.5″ OD Inconel 625 reactor supported by Inconel mesh. The catalysts were dried at 250° C. under 60 ml/min flowing nitrogen for at least 2 hours prior to pre-fluorination. HF vapour flowing at 30 ml/min was then passed over the catalyst along with 30 ml/min nitrogen at 250° C. for one hour. The nitrogen was then directed to the reactor exit leaving neat HF passing over the catalyst. The temperature was slowly ramped to 380° C. and held for 10 hours. The temperature was then reduced to 350° C. and the HF flow reduced to 25 mL/min. A co-feed of 1233xf (2-chloro-3,3,3-trifluoropropene) was fed by its own vapour pressure and the flow controlled to 1 mL/min through an orifice plate. Reactor off-gas was sampled periodically from 0.5 to 7 h of continuous running, into deionised water and analysed by GC to determine reaction progress. Results are shown in Table 11.
















TABLE 11









Average.


Conv.





Pore
BJH Ads
Activity
Product Yield
Decay
Conv.
Conv.
















Volume
Pore
1233xf
1234yf
245cb
rate
Half-life
Half-life


Catalyst
@0.99P/P°
Diameter
Conv.
mol
mol
(Stability)
(Stability)
(Stability)


Example
(cm3/g)
(Å)
(%)
(%)
(%)
k (h−1)
t0.5 (h)
t0.5 (h · g−1)


















CE16
0.284
101
27.8
18.8
5.4
0.13
5.6
2


12
0.440
147
82.8
43.6
13.9
0.04
16.5
9.7


14
0.731
199
84.3
45.4
14.3
0.12
5.8
4.5


15
0.606
205
70.9
50.8
13.6
0.13
5.5
3.4









It appears from the results shown in Table 11 that increasing the pore volume and average pore diameter of the pure chromia catalysts relative to the catalyst of Comparative Example 16 led to an increase in the catalyst activity and product yield. There was also an improvement in catalyst stability.


Production of 1234yf from 245cb


The performance of the catalyst of Examples 12, 14 and 15 was tested for the production of 1234yf from the dehydrofluorination of 245cb. The results were compared to those of a commercially available chromia catalyst (Comparative Example 17).


Each catalyst (3 mL, 0.5-1.4 mm) was charged to an 0.5″ OD Inconel 625 reactor supported by Inconel mesh. The catalysts were dried at 250° C. under 60 ml/min flowing nitrogen for at least 2 hours prior to pre-fluorination. HF vapour flowing at 30 mL/min was then passed over the catalyst along with 30 mL/min nitrogen at 250° C. for one hour. The nitrogen was then directed to the reactor exit leaving neat HF passing over the catalyst. The temperature was slowly ramped to 380° C. and held for 10 hours. The temperature was then reduced to 250° C. and the HF flow reduced to 25 mL/min. A co-feed of 245cb (1,1,1,2,3-pentafluoropropane) vapour was fed by sparging nitrogen (1 ml/min) through the liquid at 9° C. and resulting in a 245eb flow of 1 mL/min. Reactor off-gas was sampled periodically from 0.5 to 7 h of continuous running into deionised water and analysed by GC to determine reaction progress. Results are shown in Table 12.













TABLE 12








Average.





Pore
BJH Ads
Activity




Volume
Pore
245cb


Catalyst

@0.99P/P°
Diameter
Conversion


Example
Mass/g
(cm3/g)
(Å)
(%)







CE17
2.7
0.284
101
78.5


12
1.7
0.440
147
82.7


14
1.4
0.731
199
81.7


15
1.7
0.606
205
79.3









It appears from the data in Table 12 that the catalyst activity of the high pore volume and large pore catalysts was higher than that of the catalyst of Comparative Example 17. The Zn promoted catalyst of Example 15 also increased the yield of 1234yf. All of the catalysts were equally stable.


Production of 1234yf from 245eb


The performance of the catalyst of Example 12 was tested for the production of 1234yf and 245cb from the dehydrofluorination of 245eb. The results were compared to those of a commercially available chromia catalyst (Comparative Example 16).


Each catalyst (3 mL, 0.5-1.4 mm) was charged to an 0.5″ OD Inconel 625 reactor supported by Inconel mesh. The catalysts were dried at 250° C. under 60 mL/min flowing nitrogen for at least 2 hours prior to pre-fluorination. HF vapour flowing at 30 ml/min was then passed over the catalyst along with 30 mL/min nitrogen at 250° C. for one hour. The nitrogen was then directed to the reactor exit leaving neat HF passing over the catalyst. The temperature was slowly ramped to 380° C. and held for 10 hours. The temperature was then reduced to 250° C. and the HF flow reduced to 25 mL/min. A co-feed of 245eb (1,1,1,2,3-pentafluoropropane) vapour was fed by sparging nitrogen (1 mUnnin) through the liquid at 9° C. and resulting in a 245eb flow of 1 mL/min. Reactor off-gas was sampled periodically from 0.5 to 7 h of continuous running into deionised water and analysed by GC to determine reaction progress. The results are shown in Table 13.















TABLE 13










Rate of





Pore
Average.

increase in





Volume
BJH Ads
Activity
activity
Yield




@0.99P/
Pore
245eb
245eb
1234yf


Catalyst


Diameter
Conversion
Conversion
mol


Example
Mass/g
(cm3/g)
(Å)
(%)
gain (%/h)
(%)







CE16
2.7
0.284
101
18.7
0.5
15.3


12
1.7
0.440
147
36.5
6.8
22.1









It appears from the results in Table 13 that the catalyst activity and 1234yf yield was higher over the high pore volume/large pore catalyst than it was over the catalyst of Comparative Example 16. In addition the activity of the high pore volume/large pore catalyst steadily increased over time and produced a higher yield of 1234yf.


Preferences and options for a given aspect, feature or parameter of the invention should, unless the context indicates otherwise, be regarded as having been disclosed in combination with any and all preferences and options for all other aspects, features and parameters of the invention.

Claims
  • 1. A catalyst comprising one or more metal oxides, wherein the catalyst has a total pore volume equal to or greater than 0.3 cm3/g and a mean pore diameter greater than or equal to 90 Å, where in the pore volume is measured using N2 adsorption porosimetry and the mean pore diameter is measured using N2 BET adsorption porosimetry.
  • 2. A catalyst according to claim 1, wherein the total pore volume is equal to or greater than 0.4 cm3/g.
  • 3. A catalyst according to claim 1, wherein the average pore width of the catalyst is greater than or equal to 100 Å when measured by N2 BET adsorption porosimetry.
  • 4. A catalyst according to claim 1, wherein the average pore width of the catalyst is greater than or equal to 130 Å when measured by N2 BJH adsorption porosimetry.
  • 5. A catalyst according to claim 1, wherein the average pore width of the catalyst is greater than or equal to 90 Å when measured by N2 BJH desorption porosimetry.
  • 6. A catalyst according to claim 1 provided in the form of pellet or pellets comprising a plurality of catalyst particles.
  • 7. A catalyst according to claim 6, wherein the pellets comprise graphite.
  • 8. A catalyst according to claim 6, wherein the pellets have a longest dimension from about 1 mm to about 100 mm.
  • 9. A catalyst according to claim 1, wherein the metal is a transition metal.
  • 10. A catalyst according to claim 9, wherein the transition metal comprises chromium.
  • 11. A catalyst according to claim 9, wherein the transition metal comprises zinc.
  • 12. A catalyst according to claim 1 which comprises at least 80 wt % chromia.
  • 13. A catalyst according to claim 1, wherein the catalyst is unused.
  • 14. A method of preparing a catalyst as defined in claim 1, comprising the steps of: a) preparing a metal salt solution and a hydroxide solution;b) combining the solutions at a pH of greater than 7.5 in order to precipitate the metal hydroxide(s);c) drying the precipitated metal hydroxides;d) calcining the metal hydroxides to form the metal oxide(s).
  • 15. A method according to claim 14, wherein step b) is carried out at a pH of greater than 8.
  • 16. A method according to claim 15, wherein step b) is carried out at a pH of greater than or equal to 8.5.
  • 17. A method according to claim 14, wherein the metal salt comprises a nitrate salt.
  • 18. A method according to claim 14, wherein the hydroxide solution may comprise ammonium hydroxide (NH4OH).
  • 19. A method according to claim 14, wherein the metal salt solution is provided at a concentration of from about 1 mol/l to about 10 mol/l.
  • 20. A method according to claim 14, wherein the hydroxide solution is provided at a concentration of from 1 mol/l to about 10 mol/l.
  • 21. A method according to claim 14 wherein step is performed by combining the solutions in a body of solvent, such as water.
  • 22. A method according to claim 14, wherein step is carried out at a substantially constant temperature, such as from 0 to 50° C.
  • 23. A method according to claim 14, wherein step (b) is performed while agitating the combined solutions.
  • 24. A method according to claim 14, wherein the precipitate formed during step (b) preferably comprises particles having average longest dimensions of from about 5 to about 20 μm.
  • 25. A method according to claim 14, wherein step (c) includes removing liquid from the slurry of metal hydroxide precipitate(s) to produce a wet cake.
  • 26. A method according to claim 25, wherein the cake is washed prior to any drying or calcining.
  • 27. A method according to claim 25, wherein step (c) includes removing liquid, ex, residual liquid, from the wet metal hydroxide(s) cake by exposing it to elevated temperature, preferably where such elevated temperature is between 50° C. and 200° C. and more preferably may be between 80° C. and 150° C., e.g. around 90° C. to around 120° C.
  • 28. A method according to claim 27, wherein the precipitate is preferably exposed to the elevated temperature for at least 15 mins.
  • 29. A method according to claim 14, wherein step (d) includes a step of calcining the metal hydroxide, preferably after liquid removal and/or drying.
  • 30. A method according to claim 14, wherein die calcining step includes heating the metal hydroxides to a temperature between around 200° C. and around 550° C.
  • 31. A method according to claim 14, wherein the calcining step is performed for a sufficient period to produce a catalyst having a TGA loss on ignition (LOI) of less than around 15%.
  • 32. A method according to claim 14 further comprising combining the calcined metal oxide with graphite to provide a catalyst composition comprising around 0.1 wt % to around 10 wt % graphite.
  • 33. A method according to claim 14, wherein the calcined metal oxide and/or catalyst composition is pressed to form catalyst pellets.
  • 34. A method according to claim 33, wherein the pressing takes place under a load of around 1 to 100 tonnes.
  • 35. A method according to claim 34, wherein the pellets so formed have a longest dimension from about 1 mm to about 100 mm.
  • 36. A process for fluorinating a C2-3 hydrohalocarbon species, comprising contacting the species with a catalyst according to claim 1.
  • 37. A process according to claim 36, comprising contacting trichloroethylene the catalyst in the presence of HF to produce 1,1,1,2-tetrafluoroethane (134a).
  • 38. A process according to claim 36 wherein the species is a C3 hydrohalocarbon species.
  • 39. A process for dehydrohalogenating a C2-3 hydrohalocarbon species, comprising contacting the species with a catalyst according to claim 1.
  • 40. A process according to claim 39, comprising contacting a hydro(halo)fluoropropane with the catalyst to produce a fluoropropene.
  • 41. A process according to claim 40, wherein the fluoropropene is a tetrafluoropropene (1234).
  • 42. A process according to claim 41, wherein the hydro(halo)propane comprises a compound selected from t re group consisting of: 1,1,1,2,3-pentafluoropropane, 1,1,1,2,2-pentafluoropropane and/or 1,1,1,3,3-pentafluoropropane.
  • 43. A process according to claim 41, wherein the tetrafluoropropene comprises 1,3,3,3-tetrafluoropropene and/or 2,3,3,3-tetrafluoropropene.
  • 44. A process for manufacturing a tetrafluoropropene comprising contacting a hydro(halo)propene with HF in the presence of a catalyst according to claim 13.
  • 45. A process according to claim 44, wherein the hydro(halo)propene comprises a hydrochlorofluoropropene.
  • 46. A process for eliminating HF from a saturated C2-3 hydrohalocarbon species, comprising contacting the species with a catalyst according to claim 13.
  • 47. A process for adding HF to an unsaturated C2-3 hydrohalocarbon species, comprising contacting the species with a catalyst according to claim 1.
  • 48. A process according to claim 36, wherein the method is conducted in the vapour phase.
  • 49. Use of a catalyst according to claim 13 in the fluorination and/or dehydrofluorination of a C2-3 hydrohalocarbon species.
  • 50. A fluorinated catalyst according to claim 13.
Priority Claims (1)
Number Date Country Kind
1615197.9 Sep 2016 GB national
PCT Information
Filing Document Filing Date Country Kind
PCT/GB2017/052616 9/7/2017 WO 00