TW202340134A - Process for preparing alkyl methacrylates with improved yield and reduced emissions of volatile organic compounds - Google Patents
Process for preparing alkyl methacrylates with improved yield and reduced emissions of volatile organic compounds Download PDFInfo
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- TW202340134A TW202340134A TW111148939A TW111148939A TW202340134A TW 202340134 A TW202340134 A TW 202340134A TW 111148939 A TW111148939 A TW 111148939A TW 111148939 A TW111148939 A TW 111148939A TW 202340134 A TW202340134 A TW 202340134A
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- Taiwan
- Prior art keywords
- mma
- output stream
- absorption
- gaseous output
- alkyl methacrylate
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- -1 alkyl methacrylates Chemical class 0.000 title claims abstract description 169
- 238000004519 manufacturing process Methods 0.000 title abstract description 9
- 239000012855 volatile organic compound Substances 0.000 title description 16
- 238000000034 method Methods 0.000 claims abstract description 397
- VVQNEPGJFQJSBK-UHFFFAOYSA-N Methyl methacrylate Chemical compound COC(=O)C(C)=C VVQNEPGJFQJSBK-UHFFFAOYSA-N 0.000 claims abstract description 343
- 238000010521 absorption reaction Methods 0.000 claims abstract description 155
- 239000000047 product Substances 0.000 claims abstract description 103
- 230000008569 process Effects 0.000 claims abstract description 100
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 claims abstract description 89
- 239000002243 precursor Substances 0.000 claims abstract description 37
- 239000012043 crude product Substances 0.000 claims abstract description 3
- OKKJLVBELUTLKV-UHFFFAOYSA-N Methanol Chemical compound OC OKKJLVBELUTLKV-UHFFFAOYSA-N 0.000 claims description 342
- 239000007789 gas Substances 0.000 claims description 146
- 238000006243 chemical reaction Methods 0.000 claims description 128
- 239000002250 absorbent Substances 0.000 claims description 126
- 230000002745 absorbent Effects 0.000 claims description 126
- 229910052760 oxygen Inorganic materials 0.000 claims description 81
- 238000003860 storage Methods 0.000 claims description 79
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims description 71
- 239000001301 oxygen Substances 0.000 claims description 71
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 68
- 239000011541 reaction mixture Substances 0.000 claims description 67
- 230000032050 esterification Effects 0.000 claims description 66
- 238000005886 esterification reaction Methods 0.000 claims description 66
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 claims description 58
- MWFMGBPGAXYFAR-UHFFFAOYSA-N 2-hydroxy-2-methylpropanenitrile Chemical compound CC(C)(O)C#N MWFMGBPGAXYFAR-UHFFFAOYSA-N 0.000 claims description 51
- 239000007788 liquid Substances 0.000 claims description 51
- 239000000203 mixture Substances 0.000 claims description 48
- 150000001875 compounds Chemical class 0.000 claims description 38
- 239000003381 stabilizer Substances 0.000 claims description 32
- 238000012432 intermediate storage Methods 0.000 claims description 31
- 238000004821 distillation Methods 0.000 claims description 29
- RAHZWNYVWXNFOC-UHFFFAOYSA-N Sulphur dioxide Chemical compound O=S=O RAHZWNYVWXNFOC-UHFFFAOYSA-N 0.000 claims description 28
- 238000002360 preparation method Methods 0.000 claims description 27
- 238000011282 treatment Methods 0.000 claims description 25
- 230000009435 amidation Effects 0.000 claims description 21
- 238000007112 amidation reaction Methods 0.000 claims description 21
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 claims description 14
- 229910002091 carbon monoxide Inorganic materials 0.000 claims description 14
- 238000012545 processing Methods 0.000 claims description 9
- 238000010438 heat treatment Methods 0.000 claims description 7
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 claims description 4
- 229910002092 carbon dioxide Inorganic materials 0.000 claims description 2
- 239000001569 carbon dioxide Substances 0.000 claims description 2
- 230000001476 alcoholic effect Effects 0.000 claims 1
- YNSGXUFUACJPPK-UHFFFAOYSA-N methane;methyl prop-2-enoate Chemical compound C.COC(=O)C=C YNSGXUFUACJPPK-UHFFFAOYSA-N 0.000 claims 1
- FQPSGWSUVKBHSU-UHFFFAOYSA-N methacrylamide Chemical compound CC(=C)C(N)=O FQPSGWSUVKBHSU-UHFFFAOYSA-N 0.000 abstract description 39
- QAOWNCQODCNURD-UHFFFAOYSA-M hydrogensulfate Chemical compound OS([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-M 0.000 abstract description 3
- 235000011149 sulphuric acid Nutrition 0.000 abstract description 2
- 230000009102 absorption Effects 0.000 description 135
- CERQOIWHTDAKMF-UHFFFAOYSA-N Methacrylic acid Chemical compound CC(=C)C(O)=O CERQOIWHTDAKMF-UHFFFAOYSA-N 0.000 description 45
- WSFSSNUMVMOOMR-UHFFFAOYSA-N Formaldehyde Chemical compound O=C WSFSSNUMVMOOMR-UHFFFAOYSA-N 0.000 description 37
- 239000002912 waste gas Substances 0.000 description 37
- 238000009833 condensation Methods 0.000 description 31
- 230000005494 condensation Effects 0.000 description 31
- CSCPPACGZOOCGX-UHFFFAOYSA-N Acetone Chemical compound CC(C)=O CSCPPACGZOOCGX-UHFFFAOYSA-N 0.000 description 22
- LELOWRISYMNNSU-UHFFFAOYSA-N hydrogen cyanide Chemical compound N#C LELOWRISYMNNSU-UHFFFAOYSA-N 0.000 description 22
- STNJBCKSHOAVAJ-UHFFFAOYSA-N Methacrolein Chemical compound CC(=C)C=O STNJBCKSHOAVAJ-UHFFFAOYSA-N 0.000 description 21
- 239000000178 monomer Substances 0.000 description 21
- 239000012071 phase Substances 0.000 description 20
- 238000011084 recovery Methods 0.000 description 19
- 238000001816 cooling Methods 0.000 description 18
- 239000006227 byproduct Substances 0.000 description 17
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 16
- 238000012856 packing Methods 0.000 description 16
- 239000002699 waste material Substances 0.000 description 16
- 239000000376 reactant Substances 0.000 description 15
- NBBJYMSMWIIQGU-UHFFFAOYSA-N Propionic aldehyde Chemical compound CCC=O NBBJYMSMWIIQGU-UHFFFAOYSA-N 0.000 description 14
- 239000007791 liquid phase Substances 0.000 description 14
- BWLBGMIXKSTLSX-UHFFFAOYSA-N 2-hydroxyisobutyric acid Chemical class CC(C)(O)C(O)=O BWLBGMIXKSTLSX-UHFFFAOYSA-N 0.000 description 13
- 230000000052 comparative effect Effects 0.000 description 13
- 238000005406 washing Methods 0.000 description 13
- VGGSQFUCUMXWEO-UHFFFAOYSA-N Ethene Chemical compound C=C VGGSQFUCUMXWEO-UHFFFAOYSA-N 0.000 description 12
- 239000005977 Ethylene Substances 0.000 description 12
- XYVQFUJDGOBPQI-UHFFFAOYSA-N Methyl-2-hydoxyisobutyric acid Chemical compound COC(=O)C(C)(C)O XYVQFUJDGOBPQI-UHFFFAOYSA-N 0.000 description 12
- 239000000463 material Substances 0.000 description 12
- 230000003647 oxidation Effects 0.000 description 12
- 238000007254 oxidation reaction Methods 0.000 description 12
- 239000003054 catalyst Substances 0.000 description 11
- 150000002734 metacrylic acid derivatives Chemical class 0.000 description 11
- 238000000926 separation method Methods 0.000 description 11
- 238000006116 polymerization reaction Methods 0.000 description 10
- 239000000126 substance Substances 0.000 description 10
- VQTUBCCKSQIDNK-UHFFFAOYSA-N Isobutene Chemical group CC(C)=C VQTUBCCKSQIDNK-UHFFFAOYSA-N 0.000 description 9
- 230000015572 biosynthetic process Effects 0.000 description 9
- 239000013505 freshwater Substances 0.000 description 9
- 239000003921 oil Substances 0.000 description 9
- 238000000746 purification Methods 0.000 description 9
- 238000010626 work up procedure Methods 0.000 description 9
- 150000001408 amides Chemical class 0.000 description 8
- 238000006460 hydrolysis reaction Methods 0.000 description 8
- 239000000243 solution Substances 0.000 description 8
- CERQOIWHTDAKMF-UHFFFAOYSA-M Methacrylate Chemical compound CC(=C)C([O-])=O CERQOIWHTDAKMF-UHFFFAOYSA-M 0.000 description 7
- ZTQSAGDEMFDKMZ-UHFFFAOYSA-N butyric aldehyde Natural products CCCC=O ZTQSAGDEMFDKMZ-UHFFFAOYSA-N 0.000 description 7
- 230000007062 hydrolysis Effects 0.000 description 7
- 239000000543 intermediate Substances 0.000 description 7
- 238000005201 scrubbing Methods 0.000 description 7
- MYMOFIZGZYHOMD-UHFFFAOYSA-N Dioxygen Chemical compound O=O MYMOFIZGZYHOMD-UHFFFAOYSA-N 0.000 description 6
- 238000005576 amination reaction Methods 0.000 description 6
- 239000002585 base Substances 0.000 description 6
- 230000003197 catalytic effect Effects 0.000 description 6
- 229910001882 dioxygen Inorganic materials 0.000 description 6
- 229940017219 methyl propionate Drugs 0.000 description 6
- 238000004064 recycling Methods 0.000 description 6
- NLZUEZXRPGMBCV-UHFFFAOYSA-N Butylhydroxytoluene Chemical compound CC1=CC(C(C)(C)C)=C(O)C(C(C)(C)C)=C1 NLZUEZXRPGMBCV-UHFFFAOYSA-N 0.000 description 5
- FGUUSXIOTUKUDN-IBGZPJMESA-N C1(=CC=CC=C1)N1C2=C(NC([C@H](C1)NC=1OC(=NN=1)C1=CC=CC=C1)=O)C=CC=C2 Chemical compound C1(=CC=CC=C1)N1C2=C(NC([C@H](C1)NC=1OC(=NN=1)C1=CC=CC=C1)=O)C=CC=C2 FGUUSXIOTUKUDN-IBGZPJMESA-N 0.000 description 5
- RJUFJBKOKNCXHH-UHFFFAOYSA-N Methyl propionate Chemical compound CCC(=O)OC RJUFJBKOKNCXHH-UHFFFAOYSA-N 0.000 description 5
- 239000006096 absorbing agent Substances 0.000 description 5
- 238000009835 boiling Methods 0.000 description 5
- 150000002148 esters Chemical class 0.000 description 5
- 238000011049 filling Methods 0.000 description 5
- 150000002894 organic compounds Chemical class 0.000 description 5
- 239000005416 organic matter Substances 0.000 description 5
- 238000012805 post-processing Methods 0.000 description 5
- 239000003507 refrigerant Substances 0.000 description 5
- 229920006395 saturated elastomer Polymers 0.000 description 5
- 238000001179 sorption measurement Methods 0.000 description 5
- 238000012546 transfer Methods 0.000 description 5
- QIGBRXMKCJKVMJ-UHFFFAOYSA-N 1,4-Benzenediol Natural products OC1=CC=C(O)C=C1 QIGBRXMKCJKVMJ-UHFFFAOYSA-N 0.000 description 4
- ZHNUHDYFZUAESO-UHFFFAOYSA-N Formamide Chemical compound NC=O ZHNUHDYFZUAESO-UHFFFAOYSA-N 0.000 description 4
- BZLVMXJERCGZMT-UHFFFAOYSA-N Methyl tert-butyl ether Chemical compound COC(C)(C)C BZLVMXJERCGZMT-UHFFFAOYSA-N 0.000 description 4
- GYCMBHHDWRMZGG-UHFFFAOYSA-N Methylacrylonitrile Chemical compound CC(=C)C#N GYCMBHHDWRMZGG-UHFFFAOYSA-N 0.000 description 4
- 238000004140 cleaning Methods 0.000 description 4
- 239000002826 coolant Substances 0.000 description 4
- 239000002274 desiccant Substances 0.000 description 4
- 238000010586 diagram Methods 0.000 description 4
- 238000011143 downstream manufacturing Methods 0.000 description 4
- 230000000694 effects Effects 0.000 description 4
- 238000005516 engineering process Methods 0.000 description 4
- 238000004880 explosion Methods 0.000 description 4
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 4
- TZIHFWKZFHZASV-UHFFFAOYSA-N methyl formate Chemical compound COC=O TZIHFWKZFHZASV-UHFFFAOYSA-N 0.000 description 4
- 150000004986 phenylenediamines Chemical class 0.000 description 4
- AYRBHTOSHJHALD-UHFFFAOYSA-N 1-amino-2-methylpropan-1-ol Chemical compound CC(C)C(N)O AYRBHTOSHJHALD-UHFFFAOYSA-N 0.000 description 3
- PWNBRRGFUVBTQG-UHFFFAOYSA-N 1-n,4-n-di(propan-2-yl)benzene-1,4-diamine Chemical compound CC(C)NC1=CC=C(NC(C)C)C=C1 PWNBRRGFUVBTQG-UHFFFAOYSA-N 0.000 description 3
- OPLCSTZDXXUYDU-UHFFFAOYSA-N 2,4-dimethyl-6-tert-butylphenol Chemical compound CC1=CC(C)=C(O)C(C(C)(C)C)=C1 OPLCSTZDXXUYDU-UHFFFAOYSA-N 0.000 description 3
- NLHHRLWOUZZQLW-UHFFFAOYSA-N Acrylonitrile Chemical compound C=CC#N NLHHRLWOUZZQLW-UHFFFAOYSA-N 0.000 description 3
- LYCAIKOWRPUZTN-UHFFFAOYSA-N Ethylene glycol Chemical compound OCCO LYCAIKOWRPUZTN-UHFFFAOYSA-N 0.000 description 3
- NDCGVLJXFQKXOF-UHFFFAOYSA-N N-hydroxy-2-methylpropanamine Chemical compound CC(C)CNO NDCGVLJXFQKXOF-UHFFFAOYSA-N 0.000 description 3
- 229910000831 Steel Inorganic materials 0.000 description 3
- 150000001298 alcohols Chemical class 0.000 description 3
- 239000008346 aqueous phase Substances 0.000 description 3
- 238000001311 chemical methods and process Methods 0.000 description 3
- 238000007906 compression Methods 0.000 description 3
- 230000006835 compression Effects 0.000 description 3
- 238000011109 contamination Methods 0.000 description 3
- 238000009826 distribution Methods 0.000 description 3
- 238000000605 extraction Methods 0.000 description 3
- 239000002638 heterogeneous catalyst Substances 0.000 description 3
- 239000011261 inert gas Substances 0.000 description 3
- VLKZOEOYAKHREP-UHFFFAOYSA-N n-Hexane Chemical compound CCCCCC VLKZOEOYAKHREP-UHFFFAOYSA-N 0.000 description 3
- 238000006709 oxidative esterification reaction Methods 0.000 description 3
- 238000005191 phase separation Methods 0.000 description 3
- 238000011197 physicochemical method Methods 0.000 description 3
- 229920003229 poly(methyl methacrylate) Polymers 0.000 description 3
- 229920000642 polymer Polymers 0.000 description 3
- 239000004926 polymethyl methacrylate Substances 0.000 description 3
- 230000002265 prevention Effects 0.000 description 3
- 238000007086 side reaction Methods 0.000 description 3
- 229910001220 stainless steel Inorganic materials 0.000 description 3
- 239000010935 stainless steel Substances 0.000 description 3
- 239000010959 steel Substances 0.000 description 3
- 230000009466 transformation Effects 0.000 description 3
- 150000005206 1,2-dihydroxybenzenes Chemical class 0.000 description 2
- ZZMVLMVFYMGSMY-UHFFFAOYSA-N 4-n-(4-methylpentan-2-yl)-1-n-phenylbenzene-1,4-diamine Chemical compound C1=CC(NC(C)CC(C)C)=CC=C1NC1=CC=CC=C1 ZZMVLMVFYMGSMY-UHFFFAOYSA-N 0.000 description 2
- UHJVLUYSDYOULM-UHFFFAOYSA-N 4-n-(5-methylhexan-2-yl)-1-n-phenylbenzene-1,4-diamine Chemical compound C1=CC(NC(C)CCC(C)C)=CC=C1NC1=CC=CC=C1 UHJVLUYSDYOULM-UHFFFAOYSA-N 0.000 description 2
- HGINCPLSRVDWNT-UHFFFAOYSA-N Acrolein Chemical compound C=CC=O HGINCPLSRVDWNT-UHFFFAOYSA-N 0.000 description 2
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 2
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- 229940123457 Free radical scavenger Drugs 0.000 description 2
- MHAJPDPJQMAIIY-UHFFFAOYSA-N Hydrogen peroxide Chemical compound OO MHAJPDPJQMAIIY-UHFFFAOYSA-N 0.000 description 2
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 2
- BAPJBEWLBFYGME-UHFFFAOYSA-N Methyl acrylate Chemical compound COC(=O)C=C BAPJBEWLBFYGME-UHFFFAOYSA-N 0.000 description 2
- XYFCBTPGUUZFHI-UHFFFAOYSA-N Phosphine Chemical compound P XYFCBTPGUUZFHI-UHFFFAOYSA-N 0.000 description 2
- WQDUMFSSJAZKTM-UHFFFAOYSA-N Sodium methoxide Chemical compound [Na+].[O-]C WQDUMFSSJAZKTM-UHFFFAOYSA-N 0.000 description 2
- DKGAVHZHDRPRBM-UHFFFAOYSA-N Tert-Butanol Chemical compound CC(C)(C)O DKGAVHZHDRPRBM-UHFFFAOYSA-N 0.000 description 2
- GWEVSGVZZGPLCZ-UHFFFAOYSA-N Titan oxide Chemical compound O=[Ti]=O GWEVSGVZZGPLCZ-UHFFFAOYSA-N 0.000 description 2
- 230000003213 activating effect Effects 0.000 description 2
- 230000010933 acylation Effects 0.000 description 2
- 238000005917 acylation reaction Methods 0.000 description 2
- 239000003463 adsorbent Substances 0.000 description 2
- 125000005250 alkyl acrylate group Chemical group 0.000 description 2
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 description 2
- BFNBIHQBYMNNAN-UHFFFAOYSA-N ammonium sulfate Chemical compound N.N.OS(O)(=O)=O BFNBIHQBYMNNAN-UHFFFAOYSA-N 0.000 description 2
- 229910052921 ammonium sulfate Inorganic materials 0.000 description 2
- 235000011130 ammonium sulphate Nutrition 0.000 description 2
- 239000012298 atmosphere Substances 0.000 description 2
- 235000010354 butylated hydroxytoluene Nutrition 0.000 description 2
- 238000002485 combustion reaction Methods 0.000 description 2
- 238000010960 commercial process Methods 0.000 description 2
- 238000010276 construction Methods 0.000 description 2
- 239000000498 cooling water Substances 0.000 description 2
- JHIVVAPYMSGYDF-UHFFFAOYSA-N cyclohexanone Chemical compound O=C1CCCCC1 JHIVVAPYMSGYDF-UHFFFAOYSA-N 0.000 description 2
- 230000007423 decrease Effects 0.000 description 2
- 230000018044 dehydration Effects 0.000 description 2
- 238000006297 dehydration reaction Methods 0.000 description 2
- 230000005670 electromagnetic radiation Effects 0.000 description 2
- 230000007613 environmental effect Effects 0.000 description 2
- 238000001704 evaporation Methods 0.000 description 2
- 230000008020 evaporation Effects 0.000 description 2
- 229930195733 hydrocarbon Natural products 0.000 description 2
- 150000002430 hydrocarbons Chemical class 0.000 description 2
- 238000007037 hydroformylation reaction Methods 0.000 description 2
- NTQWADDNQQUGRH-UHFFFAOYSA-N hydrogen sulfate;2-methylprop-2-enoylazanium Chemical compound OS(O)(=O)=O.CC(=C)C(N)=O NTQWADDNQQUGRH-UHFFFAOYSA-N 0.000 description 2
- 239000012442 inert solvent Substances 0.000 description 2
- 238000002347 injection Methods 0.000 description 2
- 239000007924 injection Substances 0.000 description 2
- NUJOXMJBOLGQSY-UHFFFAOYSA-N manganese dioxide Chemical compound O=[Mn]=O NUJOXMJBOLGQSY-UHFFFAOYSA-N 0.000 description 2
- 239000012528 membrane Substances 0.000 description 2
- GBMDVOWEEQVZKZ-UHFFFAOYSA-N methanol;hydrate Chemical compound O.OC GBMDVOWEEQVZKZ-UHFFFAOYSA-N 0.000 description 2
- 238000006063 methoxycarbonylation reaction Methods 0.000 description 2
- 238000002156 mixing Methods 0.000 description 2
- 239000002808 molecular sieve Substances 0.000 description 2
- 229940110728 nitrogen / oxygen Drugs 0.000 description 2
- NWVVVBRKAWDGAB-UHFFFAOYSA-N p-methoxyphenol Chemical compound COC1=CC=C(O)C=C1 NWVVVBRKAWDGAB-UHFFFAOYSA-N 0.000 description 2
- 239000002245 particle Substances 0.000 description 2
- 150000002989 phenols Chemical class 0.000 description 2
- 239000004810 polytetrafluoroethylene Substances 0.000 description 2
- 229920001343 polytetrafluoroethylene Polymers 0.000 description 2
- 150000004053 quinones Chemical class 0.000 description 2
- 239000002516 radical scavenger Substances 0.000 description 2
- 239000002994 raw material Substances 0.000 description 2
- 230000001172 regenerating effect Effects 0.000 description 2
- 238000011160 research Methods 0.000 description 2
- 150000003839 salts Chemical class 0.000 description 2
- URGAHOPLAPQHLN-UHFFFAOYSA-N sodium aluminosilicate Chemical compound [Na+].[Al+3].[O-][Si]([O-])=O.[O-][Si]([O-])=O URGAHOPLAPQHLN-UHFFFAOYSA-N 0.000 description 2
- 239000007787 solid Substances 0.000 description 2
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- 238000011105 stabilization Methods 0.000 description 2
- 238000010561 standard procedure Methods 0.000 description 2
- 239000000758 substrate Substances 0.000 description 2
- 238000003786 synthesis reaction Methods 0.000 description 2
- 238000005809 transesterification reaction Methods 0.000 description 2
- 239000012808 vapor phase Substances 0.000 description 2
- URXMMZOGVMKFIM-UHFFFAOYSA-N 2-cyanopropan-2-yl hydrogen sulfate Chemical compound CC(C)(OS(O)(=O)=O)C#N URXMMZOGVMKFIM-UHFFFAOYSA-N 0.000 description 1
- DRYMMXUBDRJPDS-UHFFFAOYSA-N 2-hydroxy-2-methylpropanamide Chemical compound CC(C)(O)C(N)=O DRYMMXUBDRJPDS-UHFFFAOYSA-N 0.000 description 1
- RZVAJINKPMORJF-UHFFFAOYSA-N Acetaminophen Chemical compound CC(=O)NC1=CC=C(O)C=C1 RZVAJINKPMORJF-UHFFFAOYSA-N 0.000 description 1
- DKPFZGUDAPQIHT-UHFFFAOYSA-N Butyl acetate Natural products CCCCOC(C)=O DKPFZGUDAPQIHT-UHFFFAOYSA-N 0.000 description 1
- UXVMQQNJUSDDNG-UHFFFAOYSA-L Calcium chloride Chemical compound [Cl-].[Cl-].[Ca+2] UXVMQQNJUSDDNG-UHFFFAOYSA-L 0.000 description 1
- XFXPMWWXUTWYJX-UHFFFAOYSA-N Cyanide Chemical compound N#[C-] XFXPMWWXUTWYJX-UHFFFAOYSA-N 0.000 description 1
- 102100040287 GTP cyclohydrolase 1 feedback regulatory protein Human genes 0.000 description 1
- 101710185324 GTP cyclohydrolase 1 feedback regulatory protein Proteins 0.000 description 1
- NGEWQZIDQIYUNV-UHFFFAOYSA-N L-valinic acid Natural products CC(C)C(O)C(O)=O NGEWQZIDQIYUNV-UHFFFAOYSA-N 0.000 description 1
- 239000002033 PVDF binder Substances 0.000 description 1
- 239000004698 Polyethylene Substances 0.000 description 1
- 239000004743 Polypropylene Substances 0.000 description 1
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 1
- 238000006887 Ullmann reaction Methods 0.000 description 1
- 229910021536 Zeolite Inorganic materials 0.000 description 1
- GOPYZMJAIPBUGX-UHFFFAOYSA-N [O-2].[O-2].[Mn+4] Chemical class [O-2].[O-2].[Mn+4] GOPYZMJAIPBUGX-UHFFFAOYSA-N 0.000 description 1
- 238000009825 accumulation Methods 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 230000009471 action Effects 0.000 description 1
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- 238000003915 air pollution Methods 0.000 description 1
- 239000003513 alkali Substances 0.000 description 1
- 229910052783 alkali metal Inorganic materials 0.000 description 1
- 150000008044 alkali metal hydroxides Chemical class 0.000 description 1
- 150000001336 alkenes Chemical class 0.000 description 1
- 125000005907 alkyl ester group Chemical group 0.000 description 1
- ILRRQNADMUWWFW-UHFFFAOYSA-K aluminium phosphate Chemical compound O1[Al]2OP1(=O)O2 ILRRQNADMUWWFW-UHFFFAOYSA-K 0.000 description 1
- 150000001412 amines Chemical class 0.000 description 1
- 229910021529 ammonia Inorganic materials 0.000 description 1
- 229920000469 amphiphilic block copolymer Polymers 0.000 description 1
- 239000012752 auxiliary agent Substances 0.000 description 1
- 230000008901 benefit Effects 0.000 description 1
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- 230000009172 bursting Effects 0.000 description 1
- 239000001110 calcium chloride Substances 0.000 description 1
- 229910001628 calcium chloride Inorganic materials 0.000 description 1
- 239000000969 carrier Substances 0.000 description 1
- 239000012159 carrier gas Substances 0.000 description 1
- 239000000919 ceramic Substances 0.000 description 1
- 238000003776 cleavage reaction Methods 0.000 description 1
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- 238000002425 crystallisation Methods 0.000 description 1
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- 238000007872 degassing Methods 0.000 description 1
- 238000013461 design Methods 0.000 description 1
- 238000003795 desorption Methods 0.000 description 1
- HPNMFZURTQLUMO-UHFFFAOYSA-N diethylamine Chemical compound CCNCC HPNMFZURTQLUMO-UHFFFAOYSA-N 0.000 description 1
- 238000009792 diffusion process Methods 0.000 description 1
- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical compound O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 description 1
- 239000006185 dispersion Substances 0.000 description 1
- 239000002019 doping agent Substances 0.000 description 1
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Abstract
Description
本發明係關於一種對環境友善之用於製備甲基丙烯酸烷酯(尤其是甲基丙烯酸甲酯(MMA))的方法,其包含製備甲基丙烯酸烷酯前驅物;酯化;後處理粗製的產物且儲存純產物,其中甲基丙烯酸烷酯係藉由至少一個吸收步驟從來自該方法之氣態輸出物流回收且以合適方式再循環至該方法中。尤其,該甲基丙烯酸烷酯前驅物是MMA前驅物,例如甲基丙烯醯胺(MAA)或其氫硫酸鹽(MAA•H 2SO 4)。在根據本發明之方法的幫助下,可能獲得高產率的甲基丙烯酸烷酯(尤其是MMA),且同時降低揮發性有機化合物釋放(排放)至環境中。 尤其,本發明包含一種用於分開或聯合進行至少一個吸收步驟的方法和設備,其中負載氣態副產物和共產物和輔劑的氣態輸出物流(例如廢空氣及廢氣)係在建立理想之方法工程參數下,利用合適之接收相(吸收劑)來處理。結果,特別地,可被轉化成MMA標的產物的前驅物和中間物、或MMA本身係在該氣態輸出物流中耗盡且再循環至該方法中。 The present invention relates to an environmentally friendly method for preparing alkyl methacrylate (especially methyl methacrylate (MMA)), which includes preparing an alkyl methacrylate precursor; esterification; and post-processing crude The product and the pure product are stored, wherein the alkyl methacrylate is recovered from the gaseous output stream from the process by at least one absorption step and recycled in a suitable manner to the process. In particular, the alkyl methacrylate precursor is an MMA precursor, such as methacrylamide (MAA) or its hydrosulfate salt (MAA·H 2 SO 4 ). With the help of the process according to the invention, it is possible to obtain high yields of alkyl methacrylates (especially MMA) and at the same time reduce the release (emission) of volatile organic compounds into the environment. In particular, the present invention encompasses a method and an apparatus for separately or jointly carrying out at least one absorption step, in which a gaseous output stream (such as waste air and waste gas) loaded with gaseous by-products and co-products and auxiliaries is used to establish the ideal process engineering. Under the parameters, use the appropriate receiving phase (absorbent) to process. As a result, in particular, precursors and intermediates that can be converted into MMA target products, or MMA itself, are consumed in the gaseous output stream and recycled to the process.
將大量的甲基丙烯酸甲酯(MMA)用於製備聚合物和具有其他可聚合化合物之共聚物。再者,甲基丙烯酸甲酯是用於基於化學合成組元之甲基丙烯酸(MA)的不同的專業酯類的重要單體,其可藉由以合適醇將MMA轉酯化而製備或可藉由縮合甲基丙烯酸和醇而獲得。用於此目的所需之甲基丙烯酸可藉由利用水來水解而從MMA獲得。因此,對於極簡單、經濟且對環境友善之製造此種原料的方法極感興趣。 有多種已知之用於在工業規模上從C2、C3或C4單元開始製造甲基丙烯酸烷酯(尤其是甲基丙烯酸甲酯(MMA))的商業方法。一般的先前技術基本上在現有之評論中描述,例如K. Nagai, T. Ui (『單體MMA技術之趨勢和未來』,住友化學有限公司;基礎化學研究實驗室("Trends and Future of Monomer-MMA Technologies", Sumitomo Chemical Co. Ltd.; Basic Chemicals Research Laboratory))、S. Krill (“Viele Wege führen zum Methacrylsäuremethylester” [很多獲得甲基丙烯酸甲酯之途徑], Chem. Unserer Zeit, 2019, 53; 2019 Wiley-VCH Verlag GmbH & Co. KGaA, Weinheim)。 一般,MMA之製備方法包含將C2、C3或C4單元轉化成反應性MMA前驅物化合物,其隨後與甲醇且視情況與水反應以產生包含MMA之粗製的產物(參見圖1)。一般的反應性MMA前驅物化合物的實例在C2系之方法的情況下為甲基丙烯醛(MAL),在C3系之方法的情況下為甲基丙烯醯胺(MAA)之衍生物或2-羥基異丁酸(2-HIBA)之衍生物,且在C4系之方法的情況下為甲基丙烯酸(MA)。藉由合適順序之熱分離步驟對該包含MMA之粗製的產物的後處理一般提供純的MMA產物,其常在進一步使用前被儲存及/或輸送。為要防止聚合型沉積物及其他副產物的形成,一般將合適之穩定劑添加至MMA以供儲存。 作為用於製備MMA之基礎的C2單元 即使乙烯作為C2單元係具有良好可利用性,MMA在此基礎上僅小程度地被製造。所有具有商業相關性之C2系的方法普遍地將甲醇用於甲酯官能之形成及甲醛(FA)中間物之製備二者。因此,伴隨著乙烯之甲醇是用於C2系之製備方法的最重要原料。在藉由BASF方法從乙烯製備MMA中,藉由氫甲醯化(例如根據C. He, F. You, Ind. Eng. Chem. Res. 2014, 53, 11442-11459)獲得之丙醛(PA)首先在第一反應步驟中與甲醛(FA)反應,以產生甲基丙烯醛(MAL)(例如DE 3220858 A1)。在第二反應步驟中,該MAL在氣相中,在大氣氧的存在下,利用熱穩定性雜多酸選擇性地被轉化成甲基丙烯酸(MA),其係作為反應性MMA前驅物化合物。MA然後藉由催化性酯化與甲醇反應以產生MMA。 在所謂的ALPHA方法中,乙烯係藉由甲氧基羰基化轉化成丙酸甲酯(MP),其係作為反應性MMA前驅物化合物(例如WO 9619434 A1或EP3272733 A1)。在後續的反應步驟中,將藉由甲醇之氧化所獲得之甲醛液脫水以產生無水甲醛(FA),然後在該氣相中,利用基於混合型鋯-矽氧化物之摻雜型觸媒,與預先形成之MP反應以產生MMA。該方法常具有>94%之選擇率。 被稱為LiMA方法之該方法與該BASF方法類似的,在該第一階段中使乙烯與合成氣體反應以產生丙醛(PA),有利地在使用銠系之膦或亞磷酸鹽配位基作為觸媒下。與甲醛液之反應則幾乎定量產率地提供MAL作為反應性MMA前驅物化合物(例如WO 2016/042000 A1)。隨後,在甲醇存在下,於直接氧化酯化中,利用貴金屬系雜相觸媒(例如WO 2014/170223)將該MAL直接轉化成MMA,其中可達成高轉化率及選擇率。 作為用於製備MMA之基礎的C3單元 全球使用之商業方法是基於丙酮(C3單元)作為原料,且經常被稱為該C3方法或ACH-磺基方法。丙酮在此首先與氰化氫(HCN)反應以產生中心丙酮氰醇(ACH)中間物。將該中間物離析且使用於後續之用於製備甲基丙烯酸(MA)和MMA的方法步驟。用於藉由該硫酸系之ACH-磺基方法而從ACH開始製備MMA的一般方法係在例如US 4529816中被描述。 例如,DE 10 2006 058250描述一種用於製備甲基丙烯酸之烷酯的方法,其包含從HCN和丙酮製備ACH,純化該ACH,使用硫酸以從ACH製備甲基丙烯醯胺,在水和硫酸之混合物的存在下以烷醇酯化該甲基丙烯醯胺,以產生甲基丙烯酸,且最後純化該酯。 在該ACH-磺基方法中,在硫酸幫助下,將ACH水解以形成α-羥基異丁醯胺(2-HIBAm)及其硫酸酯(2-SIBA)。此組成步驟在相關文獻中被稱為醯胺化或水解,因為該ACH之腈基團在形式上被轉化成醯胺官能。2-HIBAm、2-SIBA、和在醯胺化中已經藉由消去(elimination)所形成之甲基丙烯醯胺硫酸鹽(MAA)則在該硫酸系之反應混合物中熱轉化成MAA且小程度地熱轉化成MA,而SIBA轉化成MAA基本上比HIBAm轉化成MAA容易。此組成步驟常被稱為轉化。該反應條件諸如熱供應和滯留時間通常必須被優化,以特別地促進在該轉化中之所需主反應(亦即SIBAàMAA)以及同樣需要之該HIBAm副產物轉化成MAA。在該轉化中所形成之氣態副產物例如一氧化碳和二氧化碳一般係從該方法排出。 在轉化後所獲得之該硫酸系之MAA溶液(反應性MMA前驅物化合物)後續可以甲醇和水酯化以產生MMA(酯化)。可選擇地,在該轉化後,硫酸系之MAA溶液可與水反應以產生甲基丙烯酸(MA)(水解)。殘餘之2-HIBAm一般在此部分地被轉化成2-羥基異丁酸甲酯(2-MHIB),但也部分地被水解成2-羥基異丁酸(2-HIBAc)。產率相關之中間物的熱裂解尤其可在該轉化時發生,但也可在該酯化步驟中發生。因此在該酯化步驟中也需要移除氣態二次成分與其他成分。 在該ACH-磺基方法之外,該先前技術也描述其他不須使用硫酸之C3系的方法變化型。因此,避免與硫酸之使用、用於其回收(硫酸回收,SAR)之工廠組件,和作為副產物之硫酸銨的形成有關的問題。例如,該多階段之三菱氣體化學方法(the multistage Mitsubishi-Gas-Chemical process(MGC))係從1980年代中期發展且在1990年代中實施。在該MGC方法的第一階段中,將氰化氫添加至丙酮上以產生ACH。之後,利用二氧化錳觸媒,將該ACH水合以產生羥基異丁醯胺(2-HIBAm)作為反應性MMA前驅物化合物(例如EP 0487853)。在該後續步驟中,在壓力下及強觸媒鹼(例如甲氧化鈉)之存在下,甲醇首先與CO均勻地反應,以產生甲酸甲酯(例如根據DE 3436608)。作為經活化之酯的甲酸甲酯然後在轉醯胺化反應中與羥基異丁醯胺反應,以產生甲醯胺和羥基異丁酸甲酯MHIB。一般,在98%之選擇率下,轉化率約85%(例如,US 5312966A)。此二產物則經常進一步被分開地處理。甲醯胺可例如在低壓和450-580℃下且利用基於磷酸鐵或磷酸鋁與多種摻雜劑的雜相觸媒來裂開,以產生氰化氫和水。HCN之產率通常約94%。HCN和水一般皆返回至該MMA方法的循環,而明顯降低對氰化氫之需求。在US 5075493、US 5371273或US 5739379中所述的,利用雜相沸石觸媒,在甲醇存在下,在該氣相中將2-MHIB分開地脫水以產生MMA,通常達到>90%之產率。在此步驟中所形成之副產物是甲基丙烯酸。 在Evonik Röhm GmbH之C3系的Aveneer方法中同樣地避免硫酸的使用。已經藉由該Andrussow、BMA或BF方法所獲得之氰化氫在此首先被轉化成ACH。該ACH與水在該第一步驟中經常利用經改質之二氧化錳觸媒(例如DE 102008044218)而實質定量產率地被水合,以產生2-HIBAm作為反應性MMA前驅物化合物。2-HIBAm然後與甲醇反應以產生2-羥基異丁酸甲酯(2-MHIB)(例如EP 2043994)。所釋出之氨在此經常被回收且作為原料再循環至HCN方法中。例如在DE 102005023975或DE 102005023976中,另一中心步驟是甲基丙烯酸和2-MHIB之催化交叉轉酯化(catalytic cross-transesterification)以產生MMA及2-羥基異丁酸(2-HIBA)。甲基丙烯酸本身係藉由所得之羥基異丁酸的催化脫水而製造。 作為用於製備MMA之基礎的C4單元 基於該等C4單元(異丁烯、甲基第三丁基醚或第三丁醇)的MMA製備方法包含將彼等轉化成該反應性MMA前驅物化合物(甲基丙烯醛和甲基丙烯酸)。尤其,以下三種C4系之方法是習知的: 所謂之串連C4直接氧化方法(住友方法)一般係在沒有中間離析甲基丙烯醛下進行。在此,在第一步驟中,MAL係從異丁烯製備,且在第三方法步驟中MA經甲醇酯化以產生MMA之前,在第二方法步驟中氧化成MA。此方法在該文獻中也被稱為『串連方法』,因為來自該第一階段之方法氣體在沒有離析該MAL中間物下,被直接氧化成MA。 在所謂之不同的C4直接氧化(三菱方法)中,與該串連方法之方式類似的,MAL係在第一方法步驟中從異丁烯製備。然後,在第三方法步驟中被蒸發且氧化成MA之前,MAL一般在不同之第二方法步驟中被離析並以液體形式純化。然後在第四方法步驟中進行經甲醇酯化以產生MMA。 朝日(Asahi)之直接梅莎(metha)方法也常被描述為直接氧化酯化方法。在此,在第一方法步驟中,MAL也在氣相中利用第一觸媒從異丁烯製備,且在第二方法步驟中被離析且中間純化。在該第三方法步驟中,MAL被直接氧化酯化成MMA,而此步驟一般係在液相中利用懸浮觸媒進行。此方法與另外二種C4方法相比,主要差異是在該氣相中之方法步驟與在該液相中之氧化步驟的結合。 所提及之該C4系的方法係在該先前技術中描述,例如S. Nakamura, H. Ichihashi之異丁烯之蒸氣相催化氧化成甲基丙烯酸(Vapor Phase Catalytic Oxidation of Isobutene to Methacrylic Acid),Stud. Surf. Sci. Catal. 1981, 7, 755-767。 MMA之儲存和穩定化 在儲存甲基丙烯酸烷酯諸如MMA時,通常需要添加合適的穩定劑以防止形成寡聚型及聚合型轉化產物。在產物之損失和汙染之外,所釋出之反應焓和放熱反應之失控風險也構成與安全性相關的態樣(例如2008年之甲基丙烯酸酯安全處置手冊、甲基丙烯酸酯製造商協會及歐洲工業會議之甲基丙烯酸酯部門團體(Methacrylate Esters Safe Handling Manual, Methacrylate Producers Association and Methacrylates Sector Group of the European Chemical Industry Council, 2008))。常使用苯酚系化合物、苯二胺化合物、醌類或兒茶酚類或者胺N-氧化物作為穩定劑。 頻繁被使用之穩定劑常是那些僅在小量游離氧存在下發揮其功能者。為有效地發揮這些穩定劑之功能,基本上需要經溶解的氧,因為彼充作起初有效之自由基清除劑。甲基丙烯酸烷酯諸如MMA因此基本上應絕不在不含氧的環境中被處置。一般在儲存槽中的液面上方提供含氧環境,以確保該穩定劑的功效。氧在此正常逐漸地被消耗以作為該自由基清除劑機轉的部分。因此,經常需要使小量之包含氧的氣體混合物例如空氣(所謂之穩定劑空氣)或具有5至21體積%之氧的氮/氧氣體混合物連續地或週期地經過該儲存槽。因為一些甲基丙烯酸烷酯蒸氣例如MMA蒸氣在室溫下與空氣形成可燃混合物,可合適地使用具有少於21體積%之氧的氣體混合物例如氮/氧氣體混合物,以降低可燃性。然而,在該甲基丙烯酸烷酯上方之氣體混合物(氣體環境)應含有至少5%之氧,以確保該穩定劑之功效。 從甲基丙烯酸烷酯之儲存所得之廢空氣通常負載甲基丙烯酸烷酯至高達飽和限度且因此從該方法排放明顯比例的有價值產物。例如,依據在25℃之儲存溫度下的MMA蒸氣壓,150 m³/h之一般氣流可能使MMA每年損失18.5噸。 其之排放和避免 甲基丙烯酸烷酯諸如MMA和從彼所衍生之轉化產物諸如MA和其他甲基丙烯酸烷酯的生產係在複合工廠中實施,其每年通常生產至高達數十萬噸之產物。在此態樣中,即使輕微的改良產率可以導致明顯的節省。尤其,含有甲基丙烯酸烷酯例如MMA、和甲醇之廢氣和廢空氣流是與產率相關的損失,其應藉由合適措施被轉化回標的產物。同樣地由於環境理由,高度需要降低揮發性有機化合物(VOCs)的氣體排放。 透過氣態輸出物流之MMA排放的最小化被額外嚴格地在法律上被規範。根據美國清淨空氣法案(US Clean Air Act),一些甲基丙烯酸酯被歸類為揮發性有機化合物(VOCs)。根據美國環境保護署在1990年的清淨空氣法律修正案(the Clean Air Act Amendment of 1990 by the US Environmental Protection Agency (EPA)),MMA被列為有害空氣汙染物。在歐盟內,MMA之處置和儲存係根據用於排放物之控制和防止的命令96-61-EC(Directive 96-61-EC),且根據REACH規範(EC No. 1907/2006),據此,必須監控並批准直接排放至大氣中。 該先前技術描述多種用於在生產和儲存MMA時防止或最小化VOC排放的預防措施。這些不僅包括純物理方法諸如吸收、吸附和冷凝,也包括結合型物理化學方法,其中MMA被轉化(經常是不可逆地)成下述物質,彼等由於其較高沸點而可比MMA更容易地從氣流分離出及/或由於其較低之反應性及/或毒性而可在不進一步處理下釋放至大氣中。 此技術之技術人員明瞭:有機化合物之蒸氣可藉由提高壓力,或根據其蒸氣壓之溫度相關性,藉由經控制之冷卻,從氣體混合物冷凝出。例如,由於溫度降低40K,MMA和甲醇之蒸氣壓一般會減少十分之一。 該先前技術描述例如不同的冷凝方法。可以間接地完成有機蒸氣之冷卻,例如利用熱交換器或藉由直接接觸,例如藉由在板塔或填充塔中該氣流之滴流,或藉由在氣流中(利用下游的除霧器)或在利用該冷卻劑操作之Venturi噴嘴(噴射)中該冷卻劑之噴射。若待冷凝之有機物質的分壓由於高的惰性氣體含量而明顯降低,則僅小部分可在特定之冷卻劑溫度下被冷凝出。這對於在室溫下負載MMA及/或甲醇之氣態輸出物流被發現是不利的,因為高的惰性氣體含量(尤其是氮含量)常需要極低的冷卻劑溫度且因此需要高度使用冷卻能量。可選擇地,經冷凝出之有機物質的比例可藉由提高在該冷凝系統中之壓力而提高,而再次需要壓縮能量。 CN 104815514 A描述藉由解聚合將聚甲基丙烯酸甲酯(PMMA)再循環,其中首先對所得之含有MMA的蒸氣進行多階段之初步冷卻且然後進行類似之壓縮和冷卻的多階段結合。在此之缺點是:需要多階段冷卻和壓縮及因此很多的能量費用。若在有機蒸氣之冷凝時所釋放之蒸發焓要在該方法中被利用(能量累積),這必然需要高的設備複雜性。 吸附耗盡在氣態輸出物流中之有機化合物的標準方法被描述於例如2001年之F. Woodard之工業廢棄物處理手冊(Industrial Waste Treatment Handbook) Butterworth-Heinemann中。藉由吸附在固態顆粒(例如活性碳)上以移除有機化合物常被使用以供移除揮發性有機化合物(VOCs)。用於處理氣流之活性碳處理系統(吸附塔)被配置成例如具有活性碳顆粒床之圓柱槽,此通常需要平行及/或連續連接數個吸附塔,以使廢床可在連續操作中被交換(例如CN 109045940 A)。 利用活性碳之吸附移除的缺點常是:負載之吸附劑必須作為廢棄物被丟棄或僅可高度複雜地被再生。在吸附MMA之情況下,再者,必須確保充分的穩定化,以防止聚合失控(例如2008年之甲基丙烯酸酯安全處置手冊、歐洲工業會議之甲基丙烯酸酯製造商協會及甲基丙烯酸酯部門團體(Methacrylate Esters Safe Handling Manual, Methacrylate Producers Association and Methacrylates Sector Group of the European Chemical Industry Council, 2008))。活性碳床因此應僅用於經耗盡MMA之廢氣。為要防止任何反沖(kickback)至所討論之儲存槽中,活性碳床必須總是額外地藉由火焰抑制系統(例如火焰阻隔體、洗滌器等)與該儲存槽隔離。也知道其他吸附劑諸如樹脂、活性氧化鋁、矽膠和分子篩。 在氣態輸出物流中吸收耗盡(吸收)有機化合物的標準方法被描述於例如2002年N.P. Cheremisinoff之空氣汙染防治之第七章-防止及控制硬體( Handbook of Air Pollution Prevention and Control, Chapter 7 - Prevention and Control Hardware), Butterworth-Heinemann的389-497頁中。在含高濃度有機物質之氣流的處理、分離和清潔中,例如在天然氣之清潔中廣泛地使用吸收方法。通常,吸收包含將有機物質溶在該氣流之液體溶劑(接收劑相或吸收劑)中。例如在逆流噴霧塔、洗滌器、具有無規填充物之塔或板塔中進行該吸收用液體與該廢氣之間的接觸。合適吸收劑之可用性常限制吸收耗盡之使用。此外,合適吸收劑應具有對蒸氣或氣體之高溶解度、低蒸氣壓、低黏度和低成本。 慣用之吸收劑包括水、礦物油或其他非揮發油。使用水以吸收具有相對高之水溶解度的VOC。經添加至該水的兩親嵌段共聚物可提高疏水性VOC在水中的溶解度,但留在該負載之吸收劑中且使彼之再利用複雜化。在使用吸收方法時的進一步考量是負載該吸收物之廢流的處理或丟棄。 WO 9627634 A1描述在烯烴聚合時,在作為吸收劑之惰性溶劑的幫助下,回收未經轉化之單體。這包含使該廢氣從該聚合方法經過洗滌器且吸收在該廢氣中所存在之未經轉化的單體以及在該惰性溶劑中之該聚合的氣態副產物。該負載之吸收劑後續在多蒸餾步驟中被處理且部分地再循環。所述之方法的缺點是複雜且能量密集的吸收劑回收。 DE 2023205 A1描述一種用於回收在單體混合物之聚合中所產生之揮發性之未經轉化的單體的方法,其中該單體混合物包含丙烯腈和不飽和單體諸如MMA,且在彼等再循環至下游的聚合反應之前不須任何進一步的純化。這包含將負載該單體之蒸氣混合物冷卻至約15℃且乾燥彼等,且然後使彼等與基本上由丙烯腈組成之液體接觸。殘餘的蒸氣混合物然後與水相接觸,伴隨該丙烯腈被該水相吸收。所述方法之缺點是:該負載單體之蒸氣混合物必須經冷卻且乾燥,而必須有高的設備複雜性和高的操作成本以供冷凍。 EP 2083020 A1描述一種用於在無預先冷卻下吸收回收未經轉化之單體的方法。在此可能藉由利用液體長鏈烴(例如己烷)之經冷卻的吸收以回收15-80%之在聚烯烴製備中未經轉化的乙烯。這包含在所吸收之乙烯的後續解吸之後,將用於吸收之烴循環以供再次吸收。所述方法之缺點是使用額外物質作為吸收劑,而必然有進一步污染的風險。 經建立之基於物理化學方法而用於使在與方法和儲存相關之廢空氣和廢氣流中的MMA排放最小化之程序係例如在例如2008年之甲基丙烯酸酯安全處置手冊、歐洲工業會議之甲基丙烯酸酯製造商協會及甲基丙烯酸酯部門團體(Methacrylate Esters Safe Handling Manual, Methacrylate Producers Association and Methacrylates Sector Group of the European Chemical Industry Council, 2008)中描述。因此,對於處理來自MMA儲存槽的廢空氣所建議之第一步驟是反應性洗滌操作。若廢氣已經保護以免高的有機汙染,則可能使用活性碳匣於最後之廢氣清潔。 相應之工業方法係例如揭示於CN 212733497 U中。這使在來自儲油場之廢空氣中的MMA從1000-2500 mg/m³耗盡至50 mg/m³,此係藉由利用風扇使該廢空氣經過經鹼操作之洗滌塔,其中該MMA首先物理溶解,且該鹼之作用立即將彼水解成甲醇和水可溶之鹼金屬甲基丙烯酸鹽。使該耗盡之廢氣經過活性碳床。此方法之缺點是:所移除之MMA不可經濟地被回收,如果有的話。 另外可能將在氣流中之有機物質氧化轉化成無害物質諸如CO 2。例如,CN 211216181 U描述使含有乙酸丁酯、環己酮及MMA之廢氣經過包含超細分之氣泡以及過氧化氫的混合物。達成耗盡>90%之該有機成分。在此之缺點是:MMA不可用於進一步處理,且超細分泡沫之提供招致高的能量費用。 CN 111359600 A描述一種利用包含奈米結構化之二氧化鈦的固定床觸媒、光敏劑和活性氧化還原系統的固定床觸媒,以氧化降解在輸出物流中之有機蒸氣的周圍壓力變化型。藉由此方法,也可將MMA從對應負載之廢空氣和廢氣移除,但不將彼回收以供進一步使用。 文件CN 112 691 513 A描述一種用於清潔包含VOC之廢氣的方法,其包含二階段吸收。例如,在此將任何含VOC之廢氣冷卻且在第一階段中以水可溶有機溶劑(例如甲醇)處理,且在第二階段中以水處理。 此外,該先前技術描述多種方法,其中結合一些上述的基礎操作,以達成回收MMA及獲得不含MMA之氣態輸出物流的目標。CN 109621676 A描述一種用於回收MMA之方法,其中來自PMMA之解聚合的MMA蒸氣首先在以-15到18℃之鹽水操作的熱交換器中被部分地冷凝出。然後將其餘之經耗盡的氣流加熱,在經包含水鹼操作之洗滌器中處理且最後送至總氧化。在此所述之方法需要高的能量費用以供在該冷卻步驟中回收MMA以及額外之用於設備和輔劑諸如用於廢氣焚化的鹼或載體氣體的成本。 總之,所述之方法無一可從MMA製備方法之對應的負載的氣態輸出物流實質完全再循環MMA和甲醇(二者為有價值材料),以及可使彼無損失地轉化成標的產物。原則上,在所述之純物理方法中,在可接受程度之成本和複雜性下,僅可從該氣態輸出物流回收不足比例的有價值材料。在所述之物理化學方法中,實情常是:所移除之MMA係藉由化學反應不可逆地結合至或轉化成其他化合物,且因此不可再循環至該生產方法中且作為有價值產物被損失。 因此仍高度需要用於製備甲基丙烯酸烷酯諸如MMA且使在氣態輸出物流例如廢空氣和廢氣流中所存在之甲基丙烯酸烷酯諸如MMA基本上完全再循環的商業方法。尤其,是要從來自該反應性MMA前驅物化合物之製備、利用甲醇之酯化及該純的甲基丙烯酸烷酯的儲存的輸出物流回收甲基丙烯酸烷酯諸如MMA。 問題本發明所解決之問題是要提供一種用於製備甲基丙烯酸烷酯(較佳是MMA)的方法,其係在低水平之資本費用和穩定之高度操作可靠性下,克服所列之該先前技術的缺點。尤其,是要持續地提高用於製備甲基丙烯酸烷酯(較佳是MMA)的低排放方法的產率。尤其,本發明所解決之問題是要在藉由C3方法(尤其是ACH磺基方法)製備時降低該MMA標的產物的釋出。原則上,是要藉由根據本發明之方法,可能在所有標準及上述甲基丙烯酸烷酯(較佳是MMA)的製備方法中處理氣態輸出物流且回收甲基丙烯酸烷酯(較佳是MMA)。 解決方法已經發現:令人意外地達成上述目的,因為在根據本發明之方法中,甲基丙烯酸烷酯(較佳是MMA)的回收係藉由氣態輸出物流(例如廢氣、廢空氣)之優化的吸收處理及所得之負載的吸收劑的有利再循環而明顯改良。這增加該製備方法之總方法產率且使揮發性有機化合物(VOC)之排放最小化。更特別地,已經發現:藉由利用包含醇(較佳是包含甲醇)之吸收劑和水性吸收劑之結合的單一階段或多階段吸收(洗滌),可能提供負載MMA之吸收劑流,其可被再循環至該製造方法中,伴隨該總產率之提高。這些負載之吸收劑流以有利方式補充或置換新鮮的醇(尤其是新鮮的甲醇)以及新鮮的水的供應至該酯化步驟。 在根據本發明之方法的幫助下,可能避免受有機物汙染之氣態輸出物流的燃燒,伴隨CO 2之形成。再者,避免外來物質供應至該方法,且可將所用之吸收劑直接使用於該方法以作為反應物流。 該方法是額外地簡單、健全且便宜,且結合降低VOC排放及提高該MMA產率的優點。 在以下詳細描述本發明及其特性特徵。 Methyl methacrylate (MMA) is used in large quantities to prepare polymers and copolymers with other polymerizable compounds. Furthermore, methyl methacrylate is an important monomer for different specialized esters based on the chemical synthesis component methacrylic acid (MA), which can be prepared by transesterification of MMA with a suitable alcohol or can be Obtained by condensation of methacrylic acid and alcohol. The methacrylic acid required for this purpose can be obtained from MMA by hydrolysis with water. Therefore, there is great interest in extremely simple, economical and environmentally friendly methods of producing such raw materials. There are several known commercial processes for the production of alkyl methacrylates, especially methyl methacrylate (MMA), on an industrial scale starting from C2, C3 or C4 units. The general prior art is basically described in existing reviews, such as K. Nagai, T. Ui ("Trends and Future of Monomer MMA Technology", Sumitomo Chemical Co., Ltd.; Basic Chemistry Research Laboratory ("Trends and Future of Monomer MMA Technology") -MMA Technologies", Sumitomo Chemical Co. Ltd.; Basic Chemicals Research Laboratory)), S. Krill ("Viele Wege führen zum Methacrylsäuremethylester" [Many ways to obtain methyl methacrylate], Chem. Unserer Zeit, 2019, 53 ; 2019 Wiley-VCH Verlag GmbH & Co. KGaA, Weinheim). Generally, methods of preparing MMA involve converting C2, C3 or C4 units into a reactive MMA precursor compound, which is subsequently reacted with methanol and optionally water to produce a crude product comprising MMA (see Figure 1). Examples of general reactive MMA precursor compounds are methacrolein (MAL) in the case of the C2-based method, and derivatives or 2-methacrylamide (MAA) in the case of the C3-based method. Derivatives of hydroxyisobutyric acid (2-HIBA), and in the case of the C4-based method, methacrylic acid (MA). Work-up of the crude MMA-containing product by a suitable sequence of thermal separation steps generally provides a pure MMA product, which is often stored and/or transported prior to further use. To prevent the formation of polymeric deposits and other by-products, suitable stabilizers are generally added to MMA for storage. The C2 unit as the basis for the preparation of MMA Even ethylene has good availability as the C2 unit, on which basis MMA is produced only to a small extent. All commercially relevant C2-based processes commonly use methanol both for the formation of methyl ester functionality and for the preparation of formaldehyde (FA) intermediates. Therefore, methanol along with ethylene is the most important raw material for the preparation method of the C2 series. In the preparation of MMA from ethylene by the BASF process, propionaldehyde (PA) is obtained by hydroformylation (e.g. according to C. He, F. You, Ind. Eng. Chem. Res. 2014, 53, 11442-11459) ) first reacts with formaldehyde (FA) in a first reaction step to produce methacrolein (MAL) (eg DE 3220858 A1). In the second reaction step, the MAL is selectively converted into methacrylic acid (MA) in the gas phase in the presence of atmospheric oxygen using a thermally stable heteropoly acid, which serves as a reactive MMA precursor compound. . MA is then reacted with methanol via catalytic esterification to produce MMA. In the so-called ALPHA process, ethylene is converted by methoxycarbonylation into methyl propionate (MP), which serves as a reactive MMA precursor compound (eg WO 9619434 A1 or EP3272733 A1). In the subsequent reaction step, the formaldehyde liquid obtained by the oxidation of methanol is dehydrated to produce anhydrous formaldehyde (FA), and then in the gas phase, a doped catalyst based on mixed zirconium-silicon oxide is used, Reacts with preformed MP to produce MMA. This method often has >94% selectivity. This method, known as the LiMA method, is similar to the BASF method in that in the first stage ethylene is reacted with a synthesis gas to produce propionaldehyde (PA), advantageously using a rhodium-based phosphine or phosphite ligand. As a catalyst. Reaction with formaldehyde solution provides MAL as a reactive MMA precursor compound in almost quantitative yield (eg WO 2016/042000 A1). Subsequently, in the presence of methanol, the MAL is directly converted into MMA in a direct oxidative esterification using a noble metal heterogeneous catalyst (such as WO 2014/170223), in which high conversion rate and selectivity can be achieved. C3 Unit The commercial method used worldwide as the basis for the preparation of MMA is based on acetone (C3 unit) as starting material and is often referred to as the C3 method or the ACH-sulfo method. Acetone here first reacts with hydrogen cyanide (HCN) to produce the central acetone cyanohydrin (ACH) intermediate. The intermediate is isolated and used in subsequent process steps for the preparation of methacrylic acid (MA) and MMA. A general method for the preparation of MMA starting from ACH by the ACH-sulfo process of the sulfuric acid system is described, for example, in US 4529816. For example, DE 10 2006 058250 describes a process for the preparation of alkyl methacrylates, which consists of preparing ACH from HCN and acetone, purifying the ACH, using sulfuric acid to prepare methacrylamide from ACH, in a mixture of water and sulfuric acid. The methacrylamide is esterified with an alkanol in the presence of a mixture to produce methacrylic acid, and the ester is finally purified. In this ACH-sulfo method, ACH is hydrolyzed with the help of sulfuric acid to form α-hydroxyisobutylamine (2-HIBAm) and its sulfate ester (2-SIBA). This compositional step is referred to in the literature as amide or hydrolysis because the nitrile group of the ACH is formally converted into a amide function. 2-HIBAm, 2-SIBA, and methacrylamide sulfate (MAA) that has been formed by elimination in the amidation are thermally converted to MAA in the sulfuric acid-based reaction mixture to a small extent. Geothermal energy is converted into MA, and SIBA into MAA is basically easier than HIBAm into MAA. This compositional step is often called transformation. The reaction conditions such as heat supply and residence time must generally be optimized to specifically promote the desired main reaction in the conversion (ie SIBA à MAA) and the equally desired conversion of the HIBAm by-product to MAA. Gaseous by-products such as carbon monoxide and carbon dioxide formed in this conversion are generally discharged from the process. The sulfuric acid-based MAA solution (reactive MMA precursor compound) obtained after conversion can subsequently be esterified with methanol and water to produce MMA (esterification). Alternatively, after this conversion, a sulfuric acid-based solution of MAA can be reacted with water to produce methacrylic acid (MA) (hydrolysis). The residual 2-HIBAm is generally partially converted to 2-hydroxyisobutyric acid methyl ester (2-MHIB) but is also partially hydrolyzed to 2-hydroxyisobutyric acid (2-HIBAc). Yield-relevant thermal cleavage of the intermediates can occur especially during the conversion, but also during the esterification step. Therefore, gaseous secondary components and other components also need to be removed in this esterification step. In addition to the ACH-sulfo process, this prior art also describes other C3-based process variations that do not require the use of sulfuric acid. Thus, problems associated with the use of sulfuric acid, the plant components for its recovery (sulfuric acid recovery, SAR), and the formation of ammonium sulfate as a by-product are avoided. For example, the multistage Mitsubishi-Gas-Chemical process (MGC) was developed from the mid-1980s and implemented in the 1990s. In the first stage of the MGC process, hydrogen cyanide is added to acetone to produce ACH. This ACH is then hydrated using a manganese dioxide catalyst to produce hydroxyisobutylamide (2-HIBAm) as a reactive MMA precursor compound (eg EP 0487853). In this subsequent step, methanol first reacts homogeneously with CO under pressure and in the presence of a strong catalytic base (eg sodium methoxide) to produce methyl formate (eg according to DE 3436608). Methyl formate as the activated ester is then reacted with hydroxyisobutylamine in a transamidation reaction to produce formamide and methyl hydroxyisobutyrate MHIB. Generally, at a selectivity of 98%, the conversion rate is about 85% (for example, US 5312966A). The two products are often further processed separately. Formamide can be cleaved, for example, at low pressure and 450-580°C and using a heterogeneous catalyst based on iron or aluminum phosphate with various dopants to produce hydrogen cyanide and water. The yield of HCN is typically about 94%. Both HCN and water are typically returned to the cycle of the MMA process, significantly reducing hydrogen cyanide requirements. Separate dehydration of 2-MHIB in the gas phase to produce MMA in the presence of methanol using heterophasic zeolite catalysts as described in US 5075493, US 5371273 or US 5739379 typically achieves >90% yields . A by-product formed during this step is methacrylic acid. The use of sulfuric acid is also avoided in the Aveneer process of the C3 series of Evonik Röhm GmbH. The hydrogen cyanide already obtained by the Andrussow, BMA or BF process is first converted into ACH. The ACH and water are hydrated in this first step, often using a modified manganese dioxide catalyst (eg DE 102008044218) in substantial quantitative yield, to produce 2-HIBAm as the reactive MMA precursor compound. 2-HIBAm is then reacted with methanol to produce methyl 2-hydroxyisobutyrate (2-MHIB) (eg EP 2043994). The ammonia released is often recovered here and recycled as feedstock to the HCN process. For example in DE 102005023975 or DE 102005023976, another central step is the catalytic cross-transesterification of methacrylic acid and 2-MHIB to produce MMA and 2-hydroxyisobutyric acid (2-HIBA). Methacrylic acid itself is produced by catalytic dehydration of the resulting hydroxyisobutyric acid. C4 Units as Base for Preparation of MMA A process for the preparation of MMA based on these C4 units (isobutylene, methyl tert-butyl ether or tert-butanol) involves converting them into the reactive MMA precursor compound (methyl tert-butyl ether). acrolein and methacrylic acid). In particular, the following three C4-based processes are known: The so-called tandem C4 direct oxidation process (Sumitomo process) is generally carried out without intermediate isolation of methacrolein. Here, MAL is prepared from isobutylene in a first step and oxidized to MA in a second method step before MA is esterified with methanol to produce MMA in a third method step. This method is also referred to as the "cascade method" in the literature because the process gas from the first stage is directly oxidized to MA without isolating the MAL intermediate. In the so-called different C4 direct oxidation (Mitsubishi process), MAL is prepared from isobutylene in a first process step, analogously to the series process. MAL is then typically isolated and purified in liquid form in a different second process step before being evaporated and oxidized to MA in a third process step. Esterification with methanol to produce MMA is then carried out in a fourth process step. Asahi's direct metha method is also often described as a direct oxidative esterification method. In a first process step, MAL is also produced from isobutylene in the gas phase using a first catalyst and is isolated and intermediately purified in a second process step. In the third method step, MAL is directly oxidized and esterified to MMA, and this step is generally performed in the liquid phase using a suspended catalyst. The main difference between this method and the other two C4 methods is the combination of process steps in the gas phase and oxidation steps in the liquid phase. The mentioned C4-based method is described in the prior art, for example, Vapor Phase Catalytic Oxidation of Isobutene to Methacrylic Acid by S. Nakamura, H. Ichihashi, Stud. Surf. Sci. Catal. 1981, 7, 755-767. Storage and Stabilization of MMA When storing alkyl methacrylates such as MMA, it is usually necessary to add suitable stabilizers to prevent the formation of oligomeric and polymeric conversion products. In addition to product loss and contamination, the release of reaction enthalpy and the risk of loss of control of exothermic reactions also constitute safety-related aspects (such as the 2008 Methacrylate Safe Handling Manual, Methacrylate Manufacturers Association Methacrylate Esters Safe Handling Manual, Methacrylate Producers Association and Methacrylates Sector Group of the European Chemical Industry Council, 2008). Phenol compounds, phenylenediamine compounds, quinones or catechols or amine N-oxides are often used as stabilizers. Frequently used stabilizers are often those that perform their function only in the presence of small amounts of free oxygen. In order for these stabilizers to function effectively, dissolved oxygen is essentially required as it acts as an initially effective free radical scavenger. Alkyl methacrylates such as MMA should therefore essentially never be disposed of in an oxygen-free environment. An oxygenated environment is generally provided above the liquid level in the storage tank to ensure the effectiveness of the stabilizer. Oxygen is normally and gradually consumed here as part of the free radical scavenger mechanism. Therefore, it is often necessary to pass continuously or periodically through the storage tank a small amount of an oxygen-containing gas mixture, such as air (so-called stabilizer air) or a nitrogen/oxygen gas mixture with 5 to 21 volume % oxygen. Because some alkyl methacrylate vapors such as MMA vapor form flammable mixtures with air at room temperature, a gas mixture having less than 21 volume % of oxygen, such as a nitrogen/oxygen gas mixture, may be suitably used to reduce flammability. However, the gas mixture (gas environment) above the alkyl methacrylate should contain at least 5% oxygen to ensure the effectiveness of the stabilizer. The waste air obtained from the storage of alkyl methacrylates often loads alkyl methacrylates up to saturation limits and therefore emits a significant proportion of valuable products from the process. For example, based on the vapor pressure of MMA at a storage temperature of 25°C, a typical airflow of 150 m³/h may cause MMA to lose 18.5 tons per year. Their emissions and avoidance The production of alkyl methacrylates such as MMA and the transformation products derived therefrom such as MA and other alkyl methacrylates is carried out in complex plants, which typically produce up to several hundred thousand tons of products per year . In this aspect, even slight improvements in yield can result in significant savings. In particular, waste gases and waste air streams containing alkyl methacrylates such as MMA, and methanol are yield-related losses, which should be converted back to the target product by suitable measures. Also for environmental reasons, there is a high need to reduce gas emissions of volatile organic compounds (VOCs). The minimization of MMA emissions via gaseous output streams is regulated extremely strictly by law. Some methacrylates are classified as volatile organic compounds (VOCs) under the US Clean Air Act. MMA is classified as a hazardous air pollutant under the Clean Air Act Amendment of 1990 by the US Environmental Protection Agency (EPA). Within the EU, MMA is handled and stored in accordance with Directive 96-61-EC for the control and prevention of emissions and in accordance with the REACH regulation (EC No. 1907/2006), in accordance with which , direct discharge to the atmosphere must be monitored and approved. This prior art describes various precautions for preventing or minimizing VOC emissions when producing and storing MMA. These include not only purely physical methods such as absorption, adsorption and condensation, but also combined physicochemical methods, in which MMA is converted (often irreversibly) into substances that can be obtained from MMA more easily than MMA due to their higher boiling points The gas stream separates and/or may be released to the atmosphere without further processing due to its lower reactivity and/or toxicity. It is clear to those skilled in the art that vapors of organic compounds can be condensed from gas mixtures by increasing the pressure, or by controlled cooling depending on the temperature dependence of their vapor pressures. For example, as the temperature decreases by 40K, the vapor pressure of MMA and methanol will generally decrease by one-tenth. This prior art describes, for example, different condensation methods. Cooling of the organic vapor can be accomplished indirectly, for example using a heat exchanger or by direct contact, for example by trickle flow of the gas stream in a plate column or packed column, or by in the gas stream (using a downstream mist eliminator) Or the injection of the coolant in a Venturi nozzle (injection) operated with the coolant. If the partial pressure of the organic matter to be condensed is significantly reduced due to the high inert gas content, only a small portion can be condensed out at a specific coolant temperature. This has been found to be disadvantageous for gaseous output streams loaded with MMA and/or methanol at room temperature, since high inert gas contents (especially nitrogen contents) often require extremely low coolant temperatures and therefore a high use of cooling energy. Alternatively, the proportion of organic matter condensed out can be increased by increasing the pressure in the condensation system, again requiring compression energy. CN 104815514 A describes the recycling of polymethyl methacrylate (PMMA) by depolymerization, wherein the resulting MMA-containing vapor is first subjected to a multi-stage preliminary cooling and then a similar multi-stage combination of compression and cooling. The disadvantage here is that multiple stages of cooling and compression are required and therefore a lot of energy expenditure. If the evaporation enthalpy released during the condensation of organic vapors is to be utilized in this process (energy accumulation), this necessarily requires a high complexity of equipment. Standard methods for adsorbing organic compounds depleted in gaseous output streams are described, for example, in F. Woodard's Industrial Waste Treatment Handbook Butterworth-Heinemann 2001. Removal of organic compounds by adsorption onto solid particles (such as activated carbon) is often used for the removal of volatile organic compounds (VOCs). Activated carbon treatment systems (adsorption towers) for treating gas streams are configured, for example, as cylindrical tanks with a bed of activated carbon particles. This usually requires parallel and/or continuous connection of several adsorption towers so that the spent beds can be adsorbed in continuous operation. Exchange (eg CN 109045940 A). A disadvantage of adsorption removal using activated carbon is often that the loaded adsorbent must be discarded as waste or can only be regenerated with a high degree of complexity. In the case of adsorbed MMA, furthermore, adequate stabilization must be ensured to prevent runaway polymerization (e.g. Manual on the Safe Handling of Methacrylates 2008, Methacrylates Manufacturers Association of the European Industry Conference and Methacrylates Sector Group (Methacrylate Esters Safe Handling Manual, Methacrylate Producers Association and Methacrylates Sector Group of the European Chemical Industry Council, 2008). Activated carbon beds should therefore only be used for MMA-depleted exhaust gases. To prevent any kickback into the storage tank in question, the activated carbon bed must always be additionally isolated from the storage tank by a flame suppression system (eg flame arresters, scrubbers, etc.). Other adsorbents such as resins, activated alumina, silica gel and molecular sieves are also known. Standard methods for absorbing depleted (absorbed) organic compounds in gaseous output streams are described, for example, in NP Cheremisinoff's 2002 Handbook of Air Pollution Prevention and Control, Chapter 7 - Prevention and Control Hardware), Butterworth-Heinemann, pages 389-497. Absorption methods are widely used in the treatment, separation and cleaning of gas streams containing high concentrations of organic matter, such as in the cleaning of natural gas. Typically, absorption involves dissolving the organic material in the liquid solvent (receiver phase or absorbent) of the gas stream. The contact between the absorption liquid and the waste gas takes place, for example, in a countercurrent spray tower, a scrubber, a tower with random packing or a plate tower. The availability of suitable absorbents often limits the use of depleted absorbents. In addition, suitable absorbents should have high solubility for vapors or gases, low vapor pressure, low viscosity and low cost. Typical absorbents include water, mineral oil or other non-volatile oils. Water is used to absorb VOCs that have relatively high water solubility. Amphiphilic block copolymers added to the water can increase the solubility of hydrophobic VOCs in the water, but remain in the loaded absorbent and complicate their reuse. A further consideration when using absorption methods is the treatment or disposal of the waste stream carrying the absorbent. WO 9627634 A1 describes the recovery of unconverted monomers during the polymerization of olefins with the aid of an inert solvent as absorbent. This involves passing the off-gas from the polymerization process through a scrubber and absorbing the unconverted monomers present in the off-gas as well as the gaseous by-products of the polymerization in the inert solvent. The loaded absorbent is subsequently processed in multiple distillation steps and partially recycled. A disadvantage of the described method is the complex and energy-intensive absorbent recovery. DE 2023205 A1 describes a process for the recovery of volatile unconverted monomers produced in the polymerization of a monomer mixture containing acrylonitrile and unsaturated monomers such as MMA, and in which It does not require any further purification before recycling to the downstream polymerization reaction. This involves cooling the monomer-loaded vapor mixture to about 15°C and drying them, and then contacting them with a liquid consisting essentially of acrylonitrile. The residual vapor mixture is then contacted with the aqueous phase, with the acrylonitrile being absorbed by the aqueous phase. Disadvantages of this method are that the monomer-laden vapor mixture must be cooled and dried, and that high equipment complexity and high operating costs are required for freezing. EP 2083020 A1 describes a method for the absorption recovery of unconverted monomers without prior cooling. It is possible here to recover 15-80% of the ethylene that is not converted in the polyolefin preparation by utilizing the cooled absorption of liquid long-chain hydrocarbons, such as hexane. This involves recycling the hydrocarbons used for absorption for re-absorption after subsequent desorption of the absorbed ethylene. The disadvantage of this method is the use of additional substances as absorbents, with the inherent risk of further contamination. Established procedures based on physicochemical methods for minimizing emissions of MMA in waste air and waste gas streams associated with processes and storage are described, for example, in the Manual on the Safe Handling of Methacrylates 2008, the European Industry Conference Described in Methacrylate Esters Safe Handling Manual, Methacrylate Producers Association and Methacrylates Sector Group of the European Chemical Industry Council, 2008. Therefore, the first step recommended for treating waste air from MMA storage tanks is a reactive scrubbing operation. If the exhaust gas has been protected from high organic contamination, an activated carbon cartridge may be used for final exhaust gas cleaning. A corresponding industrial method is disclosed in CN 212733497 U, for example. This depletes the MMA in the waste air from the oil storage site from 1000-2500 mg/m³ to 50 mg/m³ by using a fan to pass the waste air through an alkaline-operated scrubber in which the MMA is first Physically dissolves, and the action of the base immediately hydrolyzes it into methanol and water-soluble alkali metal methacrylates. The spent exhaust gas is passed through an activated carbon bed. The disadvantage of this method is that the removed MMA cannot be recycled economically, if at all. It is also possible to oxidize organic matter in the gas stream into harmless substances such as CO 2 . For example, CN 211216181 U describes passing exhaust gas containing butyl acetate, cyclohexanone and MMA through a mixture containing ultra-fine bubbles and hydrogen peroxide. Achieve consumption of >90% of the organic component. Disadvantages here are that the MMA is not available for further processing and the provision of ultra-fine foam incurs high energy costs. CN 111359600 A describes a type of ambient pressure variation that utilizes a fixed bed catalyst containing nanostructured titanium dioxide, a photosensitizer and an active redox system to oxidatively degrade organic vapor in an output stream. By this method, MMA can also be removed from the waste air and exhaust gases of the corresponding load, but it is not recovered for further use. Document CN 112 691 513 A describes a method for cleaning exhaust gases containing VOCs, which involves two-stage absorption. For example, here any VOC-containing exhaust gas is cooled and treated in a first stage with a water-soluble organic solvent (eg methanol) and in a second stage with water. In addition, this prior art describes various methods that incorporate some of the above-mentioned basic operations to achieve the goal of recovering MMA and obtaining a gaseous output stream that is free of MMA. CN 109621676 A describes a method for recovering MMA, in which the MMA vapor from the depolymerization of PMMA is first partially condensed out in a heat exchanger operated with brine at -15 to 18°C. The remaining exhausted gas stream is then heated, treated in a scrubber containing a water-alkali operation and finally sent to total oxidation. The method described here requires high energy costs for the recovery of MMA in the cooling step as well as additional costs for equipment and auxiliary agents such as bases or carrier gases for waste gas incineration. In summary, none of the methods described makes it possible to substantially completely recycle MMA and methanol (both valuable materials) from the corresponding loaded gaseous output stream of the MMA production process and to convert them without losses into the target products. In principle, in the purely physical process described, only an insufficient proportion of the valuable material can be recovered from this gaseous output stream at an acceptable level of cost and complexity. In the described physicochemical methods, it is often the case that the removed MMA is irreversibly bound to or converted into other compounds by chemical reactions and therefore cannot be recycled into the production process and is lost as a valuable product . There is therefore still a high need for commercial processes for producing alkyl methacrylates such as MMA and for substantially complete recycling of alkyl methacrylates such as MMA present in gaseous output streams such as waste air and waste gas streams. In particular, it is desirable to recover alkyl methacrylates such as MMA from the output stream from the preparation of the reactive MMA precursor compound, the esterification with methanol and the storage of the pure alkyl methacrylate. Problem The problem solved by the present invention is to provide a process for the preparation of alkyl methacrylates (preferably MMA), which overcomes the listed problems at a low level of capital costs and a stable high operational reliability. Disadvantages of Prior Technology. In particular, it is desirable to continuously increase the yield of low-emission processes for the preparation of alkyl methacrylates, preferably MMA. In particular, the problem solved by the present invention is to reduce the release of the MMA target product when prepared by the C3 method (especially the ACH sulfo method). In principle, it is possible by the method according to the invention to process the gaseous output stream and recover the alkyl methacrylate (preferably MMA) in all standard and above-mentioned preparation methods of alkyl methacrylate (preferably MMA). ). Solution It has been found that the above objects are surprisingly achieved because in the process according to the invention the recovery of alkyl methacrylate (preferably MMA) is optimized by the gaseous output stream (e.g. waste gas, waste air) The absorption process and the advantageous recycling of the resulting loaded absorbent are significantly improved. This increases the overall process yield of the preparation method and minimizes emissions of volatile organic compounds (VOC). More particularly, it has been found that by utilizing a single stage or multi-stage absorption (scrubbing) with a combination of an alcohol-containing (preferably methanol-containing) absorbent and an aqueous absorbent, it is possible to provide an MMA-loaded absorbent stream which can is recycled into the manufacturing process, with an increase in the overall yield. These loaded absorbent streams advantageously supplement or displace the supply of fresh alcohol, especially fresh methanol, and fresh water to the esterification step. With the help of the method according to the invention, it is possible to avoid the combustion of the gaseous output stream contaminated with organic matter, with the accompanying formation of CO 2 . Furthermore, the supply of foreign substances to the process is avoided, and the absorbent used can be used directly in the process as a reactant stream. This method is additionally simple, robust and cheap, and combines the advantages of reduced VOC emissions and increased yield of the MMA. The invention and its characteristic features are described in detail below.
本發明係關於一種用於製備甲基丙烯酸烷酯(較佳是甲基丙烯酸甲酯(MMA))的方法,其包含以下方法步驟:
a. 製備至少一種甲基丙烯酸烷酯前驅物化合物,其包含在第一反應階段(醯胺化)中丙酮氰醇與硫酸的反應,以產生第一反應混合物,且在第二反應階段中轉化,其包含加熱該第一反應混合物,較佳至130至200℃之範圍中的溫度,以獲得包含該甲基丙烯酸烷酯前驅物化合物和硫酸之第二反應混合物;及
b. 在第三反應階段(酯化)中使該第二反應混合物與水和醇(較佳是甲醇)反應,以獲得包含甲基丙烯酸烷酯(較佳是甲基丙烯酸甲酯)作為粗製的甲基丙烯酸烷酯產物的第三反應混合物;及
c. 在包含至少二個蒸餾步驟的後處理區中,將甲基丙烯酸烷酯(較佳是MMA)從該第三反應混合物分離,其中低沸物係在一個蒸餾步驟中,從該粗製的甲基丙烯酸烷酯產物分離,且高沸物係在另一蒸餾步驟中從該粗製的甲基丙烯酸烷酯產物分離,以獲得純的甲基丙烯酸烷酯產物(較佳是純的MMA產物)作為來自最後的蒸餾步驟的頂部餾分;及
d. 將在方法步驟c中獲得之該純的甲基丙烯酸烷酯產物儲存在至少一個儲存設備中且視情況將在方法步驟b中獲得之該第三反應混合物(粗製的甲基丙烯酸烷酯產物)中間儲存在至少一個中間儲存設備中;及
e. 藉由以至少二種液體吸收劑處理在方法步驟b、c及/或d中獲得之至少一個氣態輸出物流來吸收氣態輸出物流GS,以獲得至少一種負載甲基丙烯酸烷酯之吸收劑(較佳是至少一種負載MMA之吸收劑),其中該液體吸收劑包含至少一種包含醇(較佳是包含甲醇)的吸收劑和至少一種水性吸收劑。
更特別地,本發明係關於一種用於製備甲基丙烯酸烷酯(較佳是甲基丙烯酸甲酯(MMA))的方法,其包含上述步驟(a)至(e),其中在方法步驟(e)中處理該氣態輸出物流GS之後獲得之至少一種負載甲基丙烯酸烷酯的吸收劑係以液體形式被至少部分地進料至方法步驟b中。
在本發明之內文中,『ppm』之表示法在無進一步修飾語下,意指按重量計之ppm(例如mg/kg)。
『包含反應物、產物及/或副產物之流、相或部分』之表示法在本發明之內文中,據了解是意指所提及之化合物存在於該個別流中;例如,該反應物、產物及/或副產物之主要部分是要在對應流中被發現。原則上,在所提及之化合物之外,還可存在進一步的成分。該等成分之命名常用以闡明個別方法步驟。
在本發明之內文中,『蒸氣』或『蒸氣流』之表示法是指一個氣態方法流,例如來自蒸餾塔之氣態頂部流。
在本發明之內文中,『低沸物』之表示法是指具有比對應之甲基丙烯酸烷酯(例如MMA)低之沸點的化學化合物。在本發明之內文中,『高沸物』之表示法是指具有比對應之甲基丙烯酸烷酯(例如MMA)高之沸點的化學化合物。在本發明之內文中,『在蒸餾步驟中被分離』之表示法意指所提及之化合物係在蒸餾步驟中,於該對應混合物或對應之物質流中被耗盡。
更特別地,本發明係關於一種用於藉由ACH磺基方法製備甲基丙烯酸烷酯(特別是MMA)的方法。原則上,可能利用該氣態輸出物流之吸收後處理(吸收步驟(e)),其根據本發明也在用於製備甲基丙烯酸烷酯(尤其是MMA)的不同方法中被描述。例如,根據本發明所述之吸收可在上述C3系之方法中被利用,其中不使用硫酸作為反應物。例如,根據本發明所述之吸收可被應用於藉由三菱氣體化學方法(MGC)製備MMA,例如根據EP 0487853或藉由Aveneer方法,例如根據DE 102008044218、EP 2043994、DE 102005023975、DE 102005023976,其中2-HIBAm被獲得以作為反應性MMA前驅物化合物且與甲醇反應。
此外,根據本發明所述之吸收可被應用於藉由上述C2系之方法,例如藉由BASF方法(例如根據C. He, F. You, Ind. Eng. Chem. Res. 2014, 53, 11442-11459)製備甲基丙烯酸烷酯(尤其是MMA),其中特別地,甲基丙烯酸(MA)作為反應性MMA前驅物化合物係藉由催化酯化與甲醇反應以產生MMA。同樣可能將根據本發明所述之吸收應用於藉由上述LiMA方法(例如根據WO 2016/042000 A1和WO 2014/170223)製備甲基丙烯酸烷酯(特別是MMA)的方法,其中特別地MAL作為反應性MMA前驅物化合物係在甲醇存在下,於直接氧化酯化中,利用雜相觸媒被轉化。
此外,根據本發明所述之吸收可應用於藉由上述C4系之方法製備甲基丙烯酸烷酯(尤其是MMA),其中特別地甲基丙烯酸(MA)作為反應性MMA前驅物化合物係藉由以甲醇酯化而轉化成MMA,例如藉由住友方法之串連的C4直接氧化方法,藉由三菱方法之不同的C4直接氧化及朝日(Asahi)之直接梅莎(metha)方法。
較佳可能在根據本發明所述之吸收中,處理包含甲基丙烯酸烷酯(尤其是包含MMA)之氣態輸出物流,其係在儲存該甲基丙烯酸烷酯產物(尤其是MMA產物)的過程中所得者。更佳地,可能在根據本發明所述之吸收中處理氣態輸出物流,其係在儲存該純的甲基丙烯酸烷酯產物(尤其是該純的MMA產物)的過程中獲得,例如在分配及/或輸送成品之前獲得。一般,在儲存過程中,由於提供一種活化該穩定劑所常需之包含氧的氣體環境,此種氣態輸出物流被形成。
較佳地,在方法步驟(e)之該吸收中被處理之氣態輸出物流GS包含至少二個選自下列之氣態輸出物流
GS1 在方法步驟(a)中獲得之氣態輸出物流GS1,其包含一氧化碳和二氧化硫;
GS2 在方法步驟(b)中獲得之氣態輸出物流GS2,其包含甲基丙烯酸烷酯(較佳是MMA),特佳是1.0體積%至5.0體積%之甲基丙烯酸烷酯(較佳是MMA)以及不多於10體積%,較佳是0.1體積%至10體積%之氧,以上各情況係以該輸出物流GS2之總體積計;
GS3 在方法步驟(c)中獲得之氣態輸出物流GS3,其包含甲基丙烯酸烷酯(較佳是MMA),特佳是1.0體積%至5.0體積%之甲基丙烯酸烷酯(較佳是MMA)以及不多於10體積%,較佳是0.1體積%至10體積%之氧,以上各情況係以該輸出物流GS3之總體積計;及
GS4 在方法步驟(d)中獲得之氣態輸出物流GS4,其包含甲基丙烯酸烷酯(較佳是MMA),特佳是1.0體積%至5.0體積%之甲基丙烯酸烷酯(較佳是MMA)以及至少10體積%,較佳是10體積%至20體積%之氧,以上各情況係以該輸出物流GS4之總體積計。
在進一步較佳具體例中,在方法步驟(e)之該吸收中所處理之氣態輸出物流GS包含至少二個選自該氣態輸出物流GS2、GS3和GS4之氣態輸出物流,且該氣態輸出物流GS更佳包含所有的輸出物流GS2、GS3及GS4。該氣態輸出物流GS2、GS3和GS4可特別地作為氣態輸出氣流GS(例如經由(5))被部分地或完全地,各別地或以結合方式被導入在方法步驟(e)中之該吸收。
有利地,在方法步驟(b)、(c)及/或(d)中,將一或多種穩定劑添加至不同的物質流,以防止或降低該甲基丙烯酸烷酯(較佳是甲基丙烯酸甲酯)的聚合。例如,可能將穩定劑添加至在該酯化之後獲得之第三反應混合物。例如,可在方法步驟(d)中該儲存及/或視情況之中間儲存時添加一或多種穩定劑。
特別地,通常僅在氣態氧存在下發揮其效果之穩定劑被使用。在該氧之反應之後,所存留的是耗盡氧之空氣,其一般是在方法步驟(b)、(c)及/或(d)中獲得之廢氣,且其較佳可作為氣態輸出物流GS2、GS3及/或GS4被引導至方法步驟(e)中(例如經由(5))以供回收甲基丙烯酸烷酯之目的。較佳地,使包含氧之氣體混合物(較佳是空氣)經過在方法步驟(c)中用於後處理之設備的至少部分及/或在方法步驟(d)中之儲存設備,以提供該氧。
較佳地,該包含氧之氣體混合物之量與在該方法中之其他物質流相比是小的。該包含氧之氣體混合物之體積常是50至1500 m
3(STP)/h,較佳是100至500 m
3(STP)/h。
在方法步驟(b)之酯化中及/或在方法步驟(c)之後處理中及/或在方法步驟(d)之儲存中,較佳是使用苯酚化合物、苯二胺系化合物、醌類及/或兒茶酚類。另外可能使用胺N-氧化物(例如TEMPOL)、或所提及之穩定劑的結合。一般的穩定劑包括但不限於氫醌單甲酯(MEHQ,CAS 150-76-5)、氫醌(HQ, CAS 123-31-9)、2,4-二甲基-6-第三丁基苯酚(BDMP,DMTBP或Topanol-A® / AO30® / IONOL K78®,CAS 1879-09-0)、2,6-二-第三丁基-4-甲基苯酚(BHT/Topanol-O®, CAS 128-37-0)、包含苯二胺化合物(例如N-(1,4-二甲基戊基)-N‘-苯基-p-苯二胺(CAS 3081-01-4)、N,N‘-二異丙基-p-苯二胺(CAS 4251-01-8)、N-(1,3-二甲基丁基)-N‘-苯基-p-苯二胺(CAS 793-24-8),例如Naugard® I-4701或Santoflex
TM434PD)之化合物或混合物。
尤其在該第一反應階段(醯胺化)及/或該第二反應階段(轉化)之期間或之後,另外可能將一或多種穩定劑添加至在步驟(a)中獲得之該第一及/或第二反應混合物。較佳可能將穩定劑添加至該經冷卻之第二反應混合物。在方法步驟(a)中之該醯胺化及/或轉化時,較佳是使用酚噻嗪及其他具有類似作用之穩定劑。
在較佳具體例中,在方法步驟(c)中獲得之純的甲基丙烯酸烷酯產物及/或經獲得作為在方法步驟(b)中之粗製的甲基丙烯酸烷酯產物的第三反應混合物包含至少一種穩定劑,其一般藉由分子氧所活化;且在方法步驟(d)中,使包含氧之氣體混合物經過該儲存設備及隨意之該中間儲存設備,而在方法步驟(d)中產生至少一個氣態輸出物流GS4,其包含甲基丙烯酸烷酯(較佳是甲基丙烯酸甲酯),及至少10體積%,較佳是10體積%至20體積%,更佳是10體積%至15體積%之氧,其係以總輸出物流GS4計,其中將此氣態輸出物流GS4引導入在方法步驟(e)之吸收中。
在步驟(a)中之醯胺化和轉化
根據本發明之方法的方法步驟(a)包含在該第一反應階段中之醯胺化以及在該第二反應階段中之轉化。
一般,方法步驟(a)提供一種氣態輸出物流GS1,其尤其包含來自方法步驟(a)之該第一及/或第二反應階段的廢氣。較佳地,該氣態輸出物流GS1主要包含一氧化碳和二氧化硫;特佳地,該氣態輸出物流GS1包含70體積%至99體積%之一氧化碳及1體積%至20體積%之二氧化硫,在各自情況下係以該輸出物流GS1之總體積計。
此氣態輸出物流GS1可在方法步驟(e)之該吸收中至少部分地被處理。特別地,該氣態輸出物流GS1可在方法步驟(e)之該吸收中與至少另一選自GS2、GS3和GS4之氣態輸出物流一同被處理。在一具體例中,所有氣態輸出物流GS1、GS2、GS3及GS4係在方法步驟(e)之該吸收中至少部分地(較佳完全地)被處理。
較佳地,該氣態輸出物流GS1從該方法(例如經由(1b)和(12))部分地或完全地排出。特別地,在方法步驟(a)中獲得氣態輸出物流GS1,其包含一氧化碳和二氧化硫,其中此氣態輸出物流GS1係與在方法步驟(b)、(c)及/或(d)中獲得之氣態輸出物流分開地從該方法排出。一般,可將此排出之氣態輸出物流GS1送去焚化,例如在用於再生該硫酸之連接的工廠中。視情況,可對該排放的氣態輸出物流GS1進行廢氣洗滌及/或部分冷凝。在一較佳具體例中,來自方法步驟(a)之氣態輸出物流GS1係部分地或完全地導引至方法步驟(b)(例如經由(1b))。
在步驟(a)(醯胺化)中之第一反應階段
根據本發明之方法包含在方法步驟(a)中之丙酮氰醇(ACH)與硫酸之反應,該反應一般係在第一反應階段(醯胺化)中的一或多個反應器內,較佳在70至130℃,更佳地70至120℃之溫度範圍中,以獲得一般包含磺氧基異丁醯胺(SIBA)和甲基丙烯醯胺(MAA)之第一反應混合物。
較佳地,在該第一反應階段中使用之硫酸的濃度範圍是98.0重量%至100.5重量%,較佳地98.0重量%至100.0重量%,較佳地99.0重量%至99.9重量%。更佳地,所述之該硫酸的使用濃度是以進料至該第一反應階段的硫酸進料流的總質量計。
所用之ACH可利用已知之工業方法製備(參見例如Ullmanns Enzyklopädie der technischen Chemie (烏爾曼工業化學百科全書)之第四版第七冊)。一般,在鹼性觸媒(例如胺)存在下,在放熱反應中將氰化氫和丙酮轉化成ACH。此一方法階段係例如在DE 10 2006 058 250和DE 10 2006 059 511中被描述。
一般,ACH和硫酸之醯胺化形成作為主要產物之α-羥基異丁醯胺(HIBAm)或其硫酸氫鹽(HIBAm·H
2SO
4)、HIBAm之硫酸酯(α-磺氧基異丁醯胺,SIBA)或其硫酸氫鹽(SIBA·H
2SO
4)及甲基丙烯醯胺氫硫酸鹽(MAA·H
2SO
4),其係呈過量硫酸之溶液形式。此技術之技術人員已知:在該反應混合物中所提及之各成分的比例是可變得且依據反應條件而定。
該第一反應階段較佳係利用過量硫酸進行。該過量的硫酸尤其可用來保持低的反應混合物黏度,此可確保更快移除反應熱及更低之該反應混合物溫度。
一般,經供應之ACH流包含以該ACH流計98.0重量%至99.8重量%,較佳地98.3重量%至99.3重量%之丙酮氰醇,0.1重量%至1.5重量%,較佳地0.2重量%至1重量%之丙酮,及0.1重量%至1.5重量%,較佳地0.3重量%至1重量%之水。
較佳是使用硫酸和ACH在方法步驟(a)之第一反應階段中,其中硫酸對ACH之莫耳比率的範圍是1.2至2;較佳地1.25至1.6;更佳地1.4至1.45。
為在該第一反應階段中實施該醯胺化(水解),原則上可能使用此技術之技術人員已知之任何用於進行水解反應之反應器,例如攪拌槽反應器及環式反應器或該等反應器之結合。可選擇地,可能使用隨意地平行連接,但較佳是串聯連接之多個反應器。在一個可能的具體例中,將1至5個反應器串聯連接;較佳是使用2-3個反應器之連續配置。
在第一反應階段中,丙酮氰醇與硫酸之反應是放熱的。因此有利的是例如在合適熱交換器幫助下,大抵或至少部分地移除所得之反應熱,以獲得改良的產率。然而,通常應避免過度冷卻,以不致太明顯地提高該反應混合物之黏度,且要防止各成分之結晶及因此防止破壞性的沉積物在例如熱交換器上。一般,冷媒(尤其是冷卻用水)之溫度範圍是20至90℃,較佳是50至90℃且更佳是60至70℃。通常,在產物側上之該設備的入口/出口的溫差是約1至20℃,尤其是2至7℃。
在第一反應階段(醯胺化)中之一或多個反應器內的ACH和硫酸的轉化係在70至130℃,較佳地70至120℃,更佳地85至110℃之範圍內的溫度下進行。一般,該第一反應階段(醯胺化)可分批地及/或連續地進行。該第一反應階段較佳例如在一或多個環式反應器中連續地進行。合適反應器和方法係在例如WO 2013/143812中被描述。有利地,該第一反應階段係在二或更多個反應器之級聯,較佳二個環式反應器之級聯中進行。可選擇地,可能使用攪拌的或循環泵取之連續攪拌的槽反應器(CSTRs)、或反應器之結合中進行。
設計在該醯胺化步驟中的滯留時間,以使時間足以最大化HIBAm、SIBA、MA和MAA的產率。一般,在該等反應器中(尤其是在該環式反應器中)的靜態滯留時間的範圍是5至35分鐘,較佳是8至20分鐘。
用於該第一反應階段(醯胺化)之該等反應器(例如該等環式反應器)較佳各自包含至少一個氣體分離器(氣體出口)。一般,氣態副產物在此被分離出且被排放。一般,在該醯胺化中所形成之氣態副產物主要是一氧化碳,其較佳以廢氣流GS1之形式或作為其一部分,從該方法排出。
另外可能結合在該第一反應階段中獲得之氣態輸出物流與在該第二反應階段(轉化)獲得之氣態輸出物流。在一較佳具體例中,在該第一反應階段及/或該第二反應階段中獲得之氣態輸出物流,係在不被進料至在方法步驟(e)中之該吸收下,直接從該方法排放。
在步驟(a)中之第二反應階段(轉化)
根據本發明之方法也包含在方法步驟(a)中該第一反應混合物之轉化,該轉化包含將該第一反應混合物加熱至較佳地在下述範圍中的溫度:130至200℃,較佳地130至170℃,更佳地140至170℃,進一步較佳地140至165℃。一般,該轉化係在一或多個反應器(例如熱傳設備或轉化反應器)中進行,以獲得主要包含甲基丙烯醯胺(MMA)和硫酸之第二反應混合物。
一般,在該轉化期間,在將該第一反應混合物加熱至在130到200℃之範圍中的溫度的過程中,MAA或MAA·H
2SO
4之量係藉由使該HIBAm脫水或藉由從SIBA消除硫酸而提高,其中該第一反應混合物是包含各自主要呈氫硫酸鹽形式之SIBA、HIBAm和MAA之硫酸溶液。
該轉化在原則上可在已知之在所述之持續時間內可達成所述之溫度的反應器中進行。在此可用已知方式,例如利用蒸汽、熱水、合適之熱載體、電能或電磁輻射諸如微波輻射來供應能量。較佳是要在一或多個熱轉化設備中進行在第二反應階段中之轉化。
所用之熱媒可以是此技術之技術人員已知之任何熱媒,例如熱持久油(thermally durable oil)、鹽浴、電磁輻射、過熱水或蒸汽。較佳是使用飽和蒸汽作為熱媒。
該反應混合物在第二反應階段(轉化)中的滯留時間常是在2至15分鐘,較佳是2至10分鐘之範圍中。較佳地,該第二反應階段包含在被稱為該轉化反應器之預熱器區段中加熱該第一反應混合物以及在被稱為延遲區段中後續滯留該反應混合物,彼等尤其被絕熱地操作。在轉化之方法步驟中,有利的是極快速地且在第一定義之持續時間內,將該反應混合物加熱至所需溫度(預熱,預熱器區段),且然後使其在該溫度下歷第二定義之持續時間(滯留,延遲區段)。
與該預熱器區段類似的延遲區段可由一或多個管所組成,除了在對比之下,這些通常未預熱。該第二反應階段(轉化)和合適設備(包含預熱器區段和延遲區段)之較佳配置係在國際專利申請案PCT/EP2021/077640中被描述。
用於該轉化之熱轉化設備可進一步較佳地與一或多種氣體分離器結合。例如,在該反應混合物離開該預熱器區段之後及/或在其離開該熱轉化設備之延遲區段之後,可能將該反應混合物引導經氣體分離器。在此尤其可能從該反應混合物分離呈該氣態輸出物流GS1形式之氣態副產物。
在一較佳具體例中,在方法步驟(a)中,獲得氣態輸出物流GS1,其含有一氧化碳和二氧化硫。此氣態輸出物流GS1尤其是藉由一或多種來自該第一及/或第二反應階段及/或下游之方法步驟(例如冷卻及/或中間儲存)的氣態輸出物流所形成。
在一較佳具體例中,在該第二反應階段中獲得之主要包含甲基丙烯醯胺和硫酸之該第二反應混合物係在該轉化後,例如在利用具有溫度範圍60至100℃之冷媒的冷卻器中,被冷卻至低於120℃之溫度,較佳至90至120℃之溫度範圍。較佳地,在冷卻該第二反應混合物時,氣態副產物係至少部分地從包含一氧化碳和二氧化硫之呈氣流GS1形式的該第二反應混合物分離。
在一具體例中,該第二反應混合物(尤其是該冷卻的第二反應混合物)在作為被進料至方法步驟(b) (酯化)中之流的轉化之前,係儲存在儲存設備例如儲存槽(緩衝槽)中。因此有利地可能確保均勻進料至下游之方法步驟(b) (酯化)。其次,該中間儲存尤其允許該冷卻之第二反應混合物進一步脫氣且因此作為氣體分離器。為供冷卻該第二反應混合物,原則上可能使用已知且合適之冷媒。使用冷卻用水是有利的。一般,該冷媒具有在30至120℃之範圍中的溫度。較佳地,在該冷卻步驟(在該轉化後之氣體分離器)及/或在該轉化後之該中間儲存中獲得之氣態輸出物流GS1係完全地或部分地從該方法排出(例如作為流1c)。此外,該氣態輸出物流GS1可完全地或部分地被引導至方法步驟(b) (酯化) (例如作為流1b)中。一般,該脫氣的第二反應混合物係完全地被引導至方法步驟(b) (酯化)中。
在步驟(b) (酯化)中之第三反應階段
根據本發明之方法包含在方法步驟(b)中該第二反應混合物(一般主要包含MMA)與水和醇在第三反應階段(酯化)中反應,以獲得包含甲基丙烯酸烷酯(較佳是甲基丙烯酸甲酯)之第三反應混合物作為粗製之甲基丙烯酸烷酯產物。
在一較佳具體例中,進行主要包含MMA之該第二反應混合物與水和甲醇之反應(酯化),以獲得包含甲基丙烯酸甲酯之第三反應混合物。用於工業規模之該酯化的條件是此技術之技術人員已知的且在例如US 5,393,918中被描述。
較佳地,在方法步驟(b)中獲得氣態輸出物流GS2,其中該輸出物流GS2較佳包含1.0體積%至5.0體積%,較佳地3.0體積%至5.0體積%之甲基丙烯酸烷酯(較佳是甲基丙烯酸甲酯),以及不多於10體積%,較佳地0.1體積%至10體積%之氧,各自係以該輸出物流GS2之總體積計。
在一較佳具體例中,來自方法步驟(b)之此氣態輸出物流GS2係在方法步驟(e)之該吸收中,至少部分地被處理。特佳地,該氣態輸出物流GS2係在方法步驟(e)之吸收中與選自GS3和GS4之至少另一氣態輸出物流一同被處理。該氣態輸出物流GS2可部分地從該方法排放(例如經由(2b)和(12))。
在方法步驟(b) (酯化)之該第三反應階段中的轉化較佳係在一或多個合適的反應器中,例如在加熱的槽中進行。特別地,可能使用蒸汽加熱的槽。在一較佳具體例中,該酯化係在二或多個,例如三或四個連續槽(槽級聯)中進行。
一般,該酯化係在溫度範圍100至180℃,較佳地100至150℃下,及在壓力至高到7巴,較佳地在壓力至高到2巴下,且使用硫酸作為觸媒來進行。
該第二反應混合物較佳與過量醇(較佳地甲醇)以及水反應。主要包含甲基丙烯醯胺之該第二反應混合物的添加和醇之添加較佳是以使甲基丙烯醯胺對醇之莫耳比率在1:1.0至1:1.6之範圍中的方式進行。
較佳地,供應至該第三反應階段(酯化)的該醇係由新供應至該方法之醇(新鮮的醇)及/或在根據本發明之方法中的再循環的流(再循環流)中存在之醇所組成。較佳地,在該第三反應階段中使用之醇的至少一部分,更佳地在該第三反應階段中使用之醇的全部係以在方法步驟(e) (例如11)中獲得之負載甲基丙烯酸烷酯之吸收劑的形式被提供。一般,從廢氣洗滌器獲得呈液相之負載甲基丙烯酸烷酯的吸收劑。
一般,在該第三反應階段中添加水,其方式是使水之濃度範圍係10重量%至30重量%,較佳地15重量%至25重量%,在各自情況下係以總反應混合物計。原則上,供應至該第三反應階段(酯化)之水可來自任何來源且可包含不同的有機化合物,只要不存在對該酯化或該下游方法階段有不良效果之化合物。供應至該第三反應階段之水較佳來自在根據本發明之方法中的再循環的流(再循環流),例如來自該甲基丙酸烷酯之純化。視需要,另外可能將新鮮的水(尤其是去礦質的水或井水)供應至該第三反應階段(酯化)。
更佳地,在該第三反應階段中使用之水的至少一部分,更佳地,在該第三反應階段中使用之水的主要部分係呈在方法步驟(e)(例如11)獲得之負載甲基丙烯酸烷酯之吸收劑形式被提供。一般,獲得該負載甲基丙烯酸烷酯之吸收劑以作為來自廢氣洗滌器之水性液相。
利用甲醇之酯化一般提供包含甲基丙烯酸烷酯(較佳是MMA)、羥基異丁酸烷酯(尤其是羥基異丁酸甲酯(MHIB))、以及進一步之副產物的第三反應混合物、以及明顯量的水和未轉化的醇(例如甲醇)。
較佳地,在方法步驟(b)之該酯化中,該第三反應混合物之可蒸發部分係呈氣體形式(蒸氣)從該等反應器移除且送至進一步後處理,例如蒸餾步驟。若較佳地使用由多個反應器(例如多個槽)所組成之級聯,可能移除所得反應混合物之可蒸發部分作為每一個槽中的蒸氣流且將彼引導至進一步後處理。較佳地,只有在最後二個槽中所形成之反應混合物的可蒸發部分被移除以作為蒸氣流且被引導至進一步後處理。
在較佳具體例中,來自方法步驟(b)之此可蒸發部分係在方法步驟(e)之該吸收中至少部分地被處理以作為包含甲基丙烯酸烷酯(較佳是甲基丙烯酸甲酯)和不多於10體積%之氧的氣態輸出物流GS2。
在步驟(c)之後處理
根據本發明之方法包含,在方法步驟(c)中,將甲基丙烯酸烷酯(較佳是MMA)從在包含至少二個蒸餾步驟之後加工區中的該第三反應混合物(在酯化後獲得的)分離出,其中低沸物係在一個蒸餾步驟中從該粗製的甲基丙烯酸烷酯產物分離,且高沸物係在另一蒸餾步驟中從該粗製的甲基丙烯酸烷酯產物分離,以獲得純的甲基丙烯酸烷酯產物(較佳是純的MMA產物)作為來自最後蒸餾步驟的頂部餾分。
一般,在方法步驟(c)中,獲得氣態輸出物流GS3,其中該輸出物流GS3較佳包含1.0體積%至5.0體積%,較佳地3.0體積%至5.0體積%之甲基丙烯酸烷酯(較佳是MMA),及不多於10體積%,較佳地0.1體積%至10體積%之氧,其係以該輸出物流GS3之總體積計。
在較佳具體例中,來自方法步驟(c)之氣態輸出物流GS3係在方法步驟(e)之該吸收中至少部分地被處理。特佳地,該氣態輸出物流GS3係在方法步驟(e)之該吸收中與選自GS2和GS4之至少另一氣態輸出物流一同至少部分地被處理。該氣態輸出物流GS3可從該方法(例如經由(3b)和(12))部分地排放。
在方法步驟(c)之後處理區中,特別可能使用此技術之技術人員已知之分離步驟,尤其是精餾、萃取、汽提及/或相分離步驟。較佳地,從該第三反應混合物分離甲基丙烯酸甲酯係包含至少二個蒸餾步驟、至少二個相分離步驟及至少一個萃取步驟。例如在國際申請案PCT/EP2021/ 077488中描述後處理區之較佳執行。
該後處理較佳包含在該酯化中獲得之該第三反應混合物的良好純化。更佳地,該預先純化包含至少一個蒸餾步驟、至少一個相分離步驟及至少一個萃取步驟。該預先純化較佳包含至少一個(較佳至少二個)蒸餾步驟。更特別地,該預先純化提供純度範圍係至少85重量%的甲基丙烯酸烷酯產物,較佳是MMA產物。
較佳地,該後處理包含純度範圍係至少85重量%的甲基丙烯酸烷酯產物的良好純化,其中該良好純化包含至少一個(較佳至少二個)蒸餾步驟。更特別地,該良好純化提供純度範圍係至少99重量%的甲基丙烯酸烷酯產物,較佳是MMA產物。
特別可以獲得所需規格之純的甲基丙烯酸烷酯,其經獲得以作為來自在方法步驟(c)中之該最後蒸餾步驟之頂部餾分,且一般在方法步驟(d)中之儲存後,被引導出該方法以作為產物流(例如(14))。在一較佳具體例中,在方法步驟(c)及/或(d)中獲得之該純的甲基丙烯酸烷酯產物包含以全部純的甲基丙烯酸烷酯產物計,至少99.9重量%,較佳地至少99.95重量%之甲基丙烯酸烷酯,特別是MMA。所存在之副產物一般可為10至300 ppm之甲基丙烯腈(MAN)及/或不多於10 ppm之丙酮,在各自情況下係以該全部純的甲基丙烯酸烷酯產物計。
有利地,將一或多種穩定劑添加在方法步驟(c)之不同的物質流中,以防止或降低該甲基丙烯酸甲酯的聚合。較佳是使用藉由分子氧所活化之至少一種穩定劑。小量之包含氧的氣體混合物(較佳是空氣)較佳經過用於在方法步驟(c)中之後處理的設備的至少多個部件,以提供用於活化該穩定劑之氧。氧之反應離開經耗盡氧之氣體混合物,該氣體混合物作為廢氣離開方法步驟(c)且一般包含甲基丙烯酸烷酯產物,尤其是MMA。
在一較佳具體例中,來自方法步驟(c)之此廢氣係在方法步驟(e)之該吸收中至少部分地被處理成包含甲基丙烯酸烷酯(較佳是甲基丙烯酸甲酯)和不多於10體積%之氧的氣態輸出物流GS3。特佳地,該氣態輸出物流GS3係在方法步驟(e)之該吸收中與選自GS2和GS4之至少另一氣態輸出物流一同被處理成氣態輸出物流GS。
一般,方法步驟(b) (酯化)產生基本上由稀釋的硫酸所組成之液體廢棄物流。此廢棄物流一般係從該方法排放。該廢棄物流(尤其是與一或多個來自根據本發明之方法的水性廢棄物流一同)較佳被送至用於再生硫酸之方法或用於獲得硫酸銨之方法。
在步驟(d)中之儲存及視情況之中間儲存
根據本發明之方法包含,在方法步驟(d)中,將在方法步驟(c)中獲得之該純的甲基丙烯酸烷酯產物儲存於至少一個儲存設備中,以及視情況將在方法步驟b中獲得之該粗製的甲基丙烯酸烷酯(第三反應混合物)中間儲存於至少一種中間儲存設備中。
較佳地,該儲存或儲存設備以及視情況地該中間儲存或該中間儲存設備包含用於容納該產物(例如該純的甲基丙烯酸烷酯產物及/或該粗製的甲基丙烯酸烷酯產物)之槽(例如儲存槽d)、至少一個產物入口、至少一個產物出口及至少一個包含氧之氣體混合物的進料口以及至少一個用於耗盡氧之氣體混合物的出口,其中所儲存之產物包含至少一種藉由分子氧所活化之穩定劑。
一般,在該儲存及視情況之該中間儲存中使用之包含氧之氣體混合物的量是在50至1500 m
3(STP)/h,較佳地100至500 m
3(STP)/h之範圍中。
通常,該耗盡氧之氣體混合物包含甲基丙烯酸烷酯(尤其是MMA),且在方法步驟(e)之該吸收中被處理以作為氣態輸出物流GS4。
較佳地,在方法步驟(d)中儲存之純的甲基丙烯酸烷酯產物係經由該至少一個出口引導出以進入輸送設備中。例如,該純的甲基丙烯酸烷酯產物可被分配至輸送槽中及/或經由一或多個導管進料至下游加工操作。
一般,在方法步驟(d)中該純的甲基丙烯酸烷酯產物(較佳是該純的MMA產物)的儲存提供包含甲基丙烯酸烷酯的廢氣,較佳是包含MMA的廢氣。在一較佳具體例中,來自方法步驟(d)之廢氣係在方法步驟(e)之該吸收中至少部分地被處理以作為氣態輸出物流GS4。特佳地,該氣態輸出物流GS4係在方法步驟(e)之該吸收中,與至少另一選自GS2和GS3之氣態輸出物流一同被處理以作為氣態輸出物流GS(例如(5))。該氣態輸出物流GS4可部分地從該方法(例如經由(4b)和(12))排放。
較佳地,該氣態輸出物流GS4包含甲基丙烯酸烷酯(較佳是甲基丙烯酸甲酯)、以及以該輸出物流GS4之總體積計,至少10體積%之氧。特佳地,在方法步驟(d)中,獲得氣態輸出物流GS4,其包含0.1體積%至5.0體積%,較佳地0.2體積%至2.0體積%之甲基丙烯酸烷酯(較佳是MMA),以及至少10體積%,較佳地10體積%至20體積%,更佳地10體積%至15體積%之氧,在各自情況下係以該輸出物流GS4之總體積計。
特別地,在該氣態輸出物流GS4中,氧、甲基丙烯酸烷酯(較佳地甲基丙烯酸甲酯)及視情況之甲醇的體積比例係低於爆炸下限(LEL),該LEL係藉由在壓熱器中的點燃試驗測定,如在DIN EN 1839:2017-04中所述的。
一般,在方法步驟(d)中儲存之該純的甲基丙烯酸烷酯產物包含至少一種穩定劑,特別是至少一種藉由分子氧所活化之穩定劑。視需要,可再次將此一穩定劑添加於方法步驟(d)中。
較佳地,在方法步驟(d)中,該儲存設備及視情況之中間儲存設備經配置乾的含氧氣體環境,其覆蓋該儲存之甲基丙烯酸烷酯的表面,以提供用於活化該穩定劑之氧。例如,包含氧之氣體混合物(例如空氣)可經過該儲存設備和視情況之中間儲存設備。該氧之反應後剩下耗盡氧之氣體混合物,其離開方法步驟(d)作為廢氣且一般包含甲基丙烯酸烷酯,特別是MMA。
在本發明之內文中,在方法步驟(d)中之該儲存及視情況之中間儲存可在此技術之技術人員已知之任何儲存設備(例如儲存槽)中進行。通常可以自由地選擇該儲存設備和該視情況之中間儲存設備的容量。已經發現:根據所期望之填充和清空操作的量和頻率來調節該容量是有用的。為使操作不中斷,較佳是:最小容量為所期望之填充體積之1.5倍。
該儲存設備及該視情況之中間儲存設備的構成可例如是包含垂直外殼、平底和錐形頂端之高於地的槽。所選之設計應特別可以在填充操作時均勻地混合內容物。為避免破壞和相關產物逃逸的風險,該儲存設備和該視情況之中間儲存設備可被設立在具有足夠容量之混凝土堤的混凝土基地上。由於安全理由,該儲存設備及/或中間儲存設備及與彼等連接之任何輸送裝置應較佳總是被設立在環堤(bunded)及/或環壁(walled)區中。為供清空該儲存設備及/或該中間儲存設備,較佳的是具有經過該槽基部之接地外流管之槽型豎井(tank shaft)。該儲存設備及/或該中間儲存設備較佳主要由鋼或不鏽鋼所構成。聚乙烯、聚丙烯或氟聚合物是同樣合適的且尤其可用於密封體及配件。
該儲存設備及/或中間儲存設備較佳具有合適之安全裝置例如斥熱(heat-repellent)塗料及/或熱絕緣體,以使從環境吸收熱能最小化;用於避免透過火花(spark)輸入能量的電土(electrical earth);用於偵測溫度之裝置(例如熱電偶),以識別可能的聚合情況;用於測定填充水平以避免過度填充該儲存裝置之測量裝置;用於關閉該槽進料口之高水平開關。合適之填充水平測量裝置的實例是由鋼或不鏽鋼製成且以乾的含氧氣體沖洗之壓力差異轉換器。
在方法步驟(d)中該儲存或視情況之中間儲存應總是在比對應之甲基丙烯酸烷酯(例如MMA)在該儲存溫度之蒸氣壓高之壓力下進行。該儲存設備及/或中間儲存設備一般可具有用於壓力釋放之設備,尤其是要防止聚合反應之失控狀況所致之破壞。一般,此種用於壓力釋放之設備可包含呈接縫及/或屋頂構造形式之所要的破裂。可選擇地或另外,該儲存設備及/或中間儲存設備可配備經重壓之人孔蓋或具有低反映壓力之爆裂碟(bursting discs)。通常,該儲存設備及/或中間儲存設備可包含壓力補償閥及/或溢流設備,例如經重壓之托板閥(pallet valve)或具有撓曲膜之通氣閥、包含乙二醇之密封罐。
較佳地,在方法步驟(d)中該儲存和視情況之中間儲存是在適合使甲基丙烯酸烷酯(例如MMA)之蒸發最小化的溫度下,但較佳不必須分開的冷卻。較佳是在方法步驟(d)中,在周圍溫度下之儲存和視情況之中間儲存。
尤其,在方法步驟(d)中該儲存或視情況之中間儲存包含至少一個排氣裝置,特別是要防止腐蝕和聚合。
為要在該儲存設備及/或中間儲存設備之氣體空間中確保低的水蒸氣濃度,可使用乾燥劑。合適之乾燥劑包括例如氧化鋁、分子篩和氯化鈣。該乾燥劑可例如安裝於該排氣管中,在該用於導入該包含氧之氣體混合物之填充氣體管中或在該用於該穩定劑之入口管中。該乾燥劑較佳在合適時間間隔下,一般是每3至6個月被再生,以確保效率且防止被聚合物阻塞。
在步驟(e)中該氣態輸出物流GS之吸收
根據本發明之方法包含在方法步驟(e)中之氣態輸出物流GS的吸收,其係藉由以至少二種液體吸收劑處理在方法步驟b、c及/或d中獲得之至少一個氣態輸出物流,以獲得至少一種負載甲基丙烯酸烷酯之吸收劑,其中該液體吸收劑包含至少一種包含醇(較佳是包含甲醇)之吸收劑及至少一種水性吸收劑。
在一較佳具體例中,在方法步驟(e)中,耗盡甲基丙烯酸烷酯之氣態輸出物流係在以該至少二種液體吸收劑處理之後獲得。一般,此耗盡甲基丙烯酸烷酯之氣態輸出物流,視情況,在熱處理之後,從該方法排放(例如流(9))。較佳地,此排放之廢氣流包含每立方公尺廢氣,少於5克之甲基丙烯酸烷酯,特別是MMA。
根據本發明,在方法步驟(e)中處理該氣態輸出物流GS之後獲得之該至少一種負載甲基丙烯酸烷酯的吸收劑係以液體形式至少部分地,較佳完全地進料至方法步驟(b) (酯化)中,且視情況,部分地進料至方法步驟c。特佳地,該負載甲基丙烯酸烷酯之吸收劑構成各自呈負載甲基丙烯酸烷酯形式之該包含醇之吸收劑和該水性吸收劑的混合物。
在上述方法步驟中釋出之該包含甲基丙烯酸烷酯(例如包含MMA)之氣態輸出物流係在方法步驟(e)中與作為吸收劑之液相接觸,該液相較佳對甲基丙烯酸烷酯蒸氣(例如MMA蒸氣(接收相))具有高的吸收容量。通常,該甲基丙烯酸烷酯(例如MMA)係藉由質量傳送溶解於該液相中,且同時在該氣相中被耗盡。若該氣相只含有甲基丙烯酸烷酯(例如MMA),該氣相由於該吸收操作而完全消失。若該氣相如同在本方法中,不僅包含甲基丙烯酸烷酯(MMA),也包含進一步之具有比該甲基丙烯酸烷酯(例如MMA)低之在該吸收劑中的溶解度的氣態成分,這些會留在該氣相中且作為耗盡甲基丙烯酸烷酯(例如MMA)的氣態輸出物流離開該吸收步驟(e)。原則上,吸收可藉由該吸收劑與待吸收之物質之間的物理交互作用,且也藉由化學反應(化學吸收)來進行或促進。在方法步驟(e)中,為供在醇和水(例如甲醇和水)之幫助下移除甲基丙烯酸烷酯(例如MMA),利用所述之分子間交互作用以利該吸收操作。
原則上較佳是對個別的甲基丙烯酸烷酯(例如MMA)具有高溶解度且與其不具有任何互溶間隙(miscibility gap)的吸收劑。特佳可能使用可被不改變的導至先前步驟中且在其中幫助形成該甲基丙烯酸烷酯標的產物(例如MMA)的吸收劑。
根據本發明,在方法步驟(e)中使用至少一種包含醇(較佳是包含甲醇)之吸收劑。特佳地,此包含醇之吸收劑含有以全部之包含醇的吸收劑計,至少50重量%,較佳地至少80重量%,更佳地至少95重量%之醇(較佳是甲醇)。在一較佳具體例中,該包含醇之吸收劑包含至少99重量%之甲醇。
為製備其他的甲基丙烯酸烷酯,較佳使用對應之醇作為吸收劑。有利地,該負載甲基丙烯酸烷酯和包含醇之吸收劑可直接被導至酯化之方法步驟(b)中,其中彼與該反應性MMA前驅物化合物(較佳是MAA)反應,以產生甲基丙烯酸烷酯(例如MMA)。
根據本發明,方法步驟(e)另外包含以至少一種水性吸收劑處理該氣態輸出物流GS。一般,此水性吸收劑包含以該全部水性吸收劑計,至少50重量%,較佳至少80重量%,更佳至少95重量%之水。特別地,可能使用去礦質之水或自來水作為水性吸收劑。
在一較佳具體例中,在方法步驟(e)中之吸收包含:
至少一個吸收步驟(e1),其中該氣態輸出物流GS係以包含至少50重量%之醇(較佳是甲醇)的第一液體之包含醇的吸收劑處理,以獲得負載甲基丙烯酸烷酯之吸收劑及富醇之氣流;及
至少一個第二吸收步驟(e2),其中富醇之氣流(來自(e1))係以包含至少50重量%之水的第二水性吸收劑處理,以獲得負載醇之水性吸收劑。
通常,利用該第二水性吸收劑的第二吸收步驟(e2)意圖要將該醇(尤其是甲醇)從在該第一吸收步驟(e1)中獲得之該富醇之氣流轉移至該水相(接收相)中。該負載醇之吸收劑較佳可引導至在方法步驟(b)的酯化中。
較佳地,在該第二吸收步驟(e2)中獲得之該負載醇之水性吸收劑及在該第一吸收步驟(e2)中獲得之該負載甲基丙烯酸烷酯之吸收劑係至少部分地進料至方法步驟(b) (酯化)以及視情況地部分進料至方法步驟(c)中。在此,來自(e1)及(e2)之該二種負載的吸收劑可能分開地或結合地被再循環。在一較佳具體例中,該二種負載之吸收劑被完全地再循環至在方法步驟(b)之該酯化中。特別地,因此可能減少在該酯化中所需之新鮮之醇和新鮮之水的量。
該第一吸收步驟(e1)及該第二吸收步驟(e2)可在至少二個不同之分開的吸收設備(洗滌設備)中或在一個吸收設備中進行。
在一較佳具體例中,在方法步驟(e)中之該吸收包含以下步驟:
(e1)在第一吸收設備中,以包含至少50重量%之醇(較佳是甲醇)之包含醇之液體吸收劑處理氣態輸出物流GS(較佳是在方法步驟b、c及/或d中獲得之一或多個氣態輸出物流),以獲得富醇之氣流,及
(e2)在第二吸收設備中,以包含至少50重量%之水的水性吸收劑處理在方法步驟(e1)中獲得之富醇的氣流。
在另一較佳具體例中,在方法步驟(e)中之該吸收係在單一吸收設備中,藉由以下方式進行:將在方法步驟b、c及/或d中獲得之一或多個氣態輸出物流進料於該吸收設備之下部中且將該至少二種液體吸收劑添加於該設備之上部中,較佳在不同點上。在本文中,該氣態輸出物流和該至少二種吸收劑較佳逆流地被導引。
在進一步較佳具體例中,在方法步驟(e)中之該吸收係在單一吸收設備中進行,其中
在方法步驟b、c及/或d中獲得之一或多個氣態輸出物流被進料於該吸收設備之下部中;
在第一吸收步驟(e1)中,包含至少50重量%之醇(較佳是甲醇)之包含醇的液體吸收劑被進料於該氣態輸出物流之進料口上方;
在第二吸收步驟(e2)中,包含至少50重量%之水的至少一種水性吸收劑被進料於該包含醇之吸收劑的進料口上方;
且其中該氣態輸出物流和該至少二種吸收劑係逆流地被導引。
特別地,在此該單一的吸收設備是包含至少二個不同結構化填料(尤其是用於以甲醇吸收MMA之結構化填料和用於以水吸收甲醇之結構化填料)的分離設備。
另外可能:該至少一種包含醇(較佳是包含甲醇)之吸收劑和該至少一種水性吸收劑係呈混合物形式一同被進料至在方法步驟(e)的吸收中,例如至該單一吸收設備中。
較佳地,在方法步驟(e)之該吸收中,該氣態輸出物流GS係以每m³之氣態輸出物流GS 0.1至5.0 kg之液體吸收劑(以該吸收劑之總和計)且在5至40℃之溫度下處理。較佳地,用於在方法步驟(e)之吸收的該至少二種吸收劑具有在5至30℃之範圍中的溫度,且在方法步驟(e)中進行該吸收操作時建立5至40℃之溫度。
在方法步驟(e)之該吸收中,可能使用此技術之技術人員已知之慣常的吸收設備。特別地,可能使用此技術之技術人員已知之在例如空氣品質管理時使用的氣液接觸設備(洗滌器)。這些一般可以有多重類型和尺寸,以藉由質量傳送(擴散)且將彼等轉移到液相而從氣流移除一或多種氣態成分。該氣相和該液相可在根據本發明使用之洗滌器中,以不同的方式彼此接觸。在第一可能的構造具體例中,例如在具有轉移盤之塔式吸收器、泡罩塔、槽類型吸收器或分散攪拌器中,該氣體被分散至相關的接收液相(吸收劑)中。在進一步可能的具體例中,該接收液相(吸收劑)可噴灑至該相關氣體中,例如在不含內部裝置之空置空間洗滌器中,諸如在Venturi、注射器、噴霧器、環形間隙或輻射流動洗滌器、或具有旋轉內部裝置的洗滌器諸如旋轉、交叉噴霧或板型洗滌器中。
在方法步驟(e)之該吸收中使用的吸收設備較佳是此技術之技術人員已知之慣常的氣液接觸設備,其中相關之氣相和相關之接收相(吸收劑)的膜在該膜於例如固定或移動基材上展開下接觸。這些的實例是具有無規填料或結構化填料的塔型吸收器、流化床吸收器、或滴流膜或表面吸收器。這些吸收設備一般的特徵是約2至5毫巴/公尺的低壓力降,可以有可變的氣體速度及與板塔類似地,可以實現高的理論板數目。
在一較佳具體例中,在方法步驟(e)中使用之吸收設備是在氣體吸收中常用之填充塔。這些係例如由圓柱塔構成,其在底部提供氣體入口和分布空間,在頂部提供液體入口和分布空間,以及在底部和頂部提供液體和氣體出口。一般,該塔包含板、篩、盤、無規填料或結構化填料,彼等一般由化學惰性之固體材料製成。
例如,在方法步驟(e)中之吸收可在具有滴流流動之填充塔中進行,其中該液體吸收劑(接收相)從該頂部流遍該填料且順流地將彼潤濕。該氣態輸出物流通常從底部進入該塔,被遍布該盤區,且與該液體吸收劑逆流地,向上流經在該填料中的間隙。可以對該塔提供外部冷卻,以進一步提高吸收水平。該塔的填料可以是較佳具有低的填充密度的任何材料,其對所用之液體是化學惰性的。合適之材料是例如鋼、不鏽鋼、瓷器、玻璃、陶瓷或PTFE、及PTFE/PFA/PVDF襯底之GFRP材料。有利地,可能使用具有規則形狀單元的床諸如環、格網、螺旋管及粉碎的固體。
原則上,在方法步驟(e)中之該吸收可在逆流設備、同流設備中或在逆流和同流設備之結合中進行。一般,同流吸收可藉由使用噴射泵或噴嘴來實施。在此情況下,待處理之廢氣與細分之液體吸收劑接觸,以提供用於質量傳送之最大表面積。
[圖之說明]
圖1描述從反應性MMA前驅物化合物(其可選擇性地從C2單元乙烯、C3單元丙酮、或C4單元異丁烯製造)形成甲基丙烯酸甲酯的高度廣泛的反應網絡。
在該BASF方法中,從乙烯開始,彼首先被氫甲醯化,且所得之丙醛與藉由甲醇之氧化所形成之甲醛縮合,以產生甲基丙烯醛。氣相氧化獲得甲基丙烯酸作為反應性MMA前驅物化合物,其可以甲醇直接酯化以產生MMA。在該α方法中,該反應性MMA前驅物化合物丙酸甲酯係藉由甲氧基羰化,直接從乙烯形成,且與藉由甲醇之氧化所形成之甲醛縮合,以產生MMA。
在該LiMA方法中,與藉由氫甲醯化及後續之與得自乙烯之甲醛的縮合的該BASF方法類似地形成的甲基丙烯醛(反應性MMA前驅物化合物)係以甲醇直接氧化酯化以產生MMA。
在C3系之方法中,從丙酮和氰化氰開始,首先在添加鹼性觸媒(例如二乙胺Et
2NH或鹼金屬氫氧化物)下製備丙酮氰醇(ACH)。在該ACH磺基方法中,該丙酮氰醇係在數個反應步驟中與硫酸反應,以產生該反應性MMA前驅物化合物甲基丙烯醯胺氫硫酸鹽(MAA·H
2SO
4),其後續藉由水解轉化成甲基丙烯酸(MA)或藉由以甲醇(MeOH)酯化成甲基丙烯酸甲酯(MMA)。可選擇地,透過藉由水解而從ACH獲得的該反應性MMA前驅物化合物2-HIBAm,進行該Aveneer方法和該三菱氣體化學方法。
從該C4單元異丁烯開始,其首先可在氣相氧化中被轉化成甲基丙烯醛,且甲基丙烯醛而後與該BASF方法之第三階段中類似的,在進一步之氣相反應中被氧化,以產生該反應性MMA前驅物化合物甲基丙烯酸。後續以甲醇酯化依序地產生MMA。
MMA也可以其他醇類轉酯化以產生甲基丙烯酸烷酯,伴隨甲醇的釋出。根據所選之方法變化型,藉由水解從MMA另外製備甲基丙烯酸是另外地經濟可行的。
圖2 (用於比較用實例V1和V2之方案)顯示MMA之製備流程圖,其包含以下方法步驟:
a製備反應性MMA前驅物化合物,
b使該反應性MMA前驅物化合物與甲醇反應,以產生粗製的MMA產物,
c熱純化該粗製的MMA產物,以產生純的MMA產物以及
d儲存該純的MMA產物,以及
f在縮合
f中處理從所提及之方法步驟所得之氣態輸出物流。
方法步驟
a包含在反應器
a中藉由丙酮氰醇
16(ACH)與硫酸
17之醯胺化和轉化的反應,製備甲基丙烯醯胺(MAA)、甲基丙烯酸(MA)和作為MMA前驅物化合物之羥基異丁醯胺(HIBA)的混合物。從方法步驟
a獲得包含一氧化碳和包含二氧化硫之氣流
GS1。氣流
GS1可經由
1b進料至在方法步驟
b中之該酯化及/或經由
1c和
12從該方法排出及/或可經由
1a和
5進料至該縮合步驟
f。
隨後,在反應器
b(方法步驟b)中,藉由酯化使所得之第二反應混合物與甲醇
6和水
8反應,以獲得粗製的MMA產物(第三反應混合物)。將較佳包含不多於10體積%之氧的包含MMA之氣流
GS2從方法步驟
b引導出。氣流
GS2可經由
2b和
12從該方法排出及/或可經由
2a和
5進料至該縮合步驟
f。
在該設備
c(方法步驟c)中,對該粗製的MMA產物進行熱後處理,伴隨從該粗製的MMA產物分離MMA,其中低沸物係在第一蒸餾步驟中,從該粗製的MMA產物分離,且高沸物係在第二蒸餾步驟中,從該粗製的MMA產物分離,以獲得純的MMA產物
13作為頂部餾分。將較佳包含不多於10體積%之氧的包含MMA之氣流
GS3從方法步驟
c導出。氣流
GS3可經由
3b和
12從該方法排出及/或可經由
3a和
5進料至該縮合步驟
f。
隨後,將該純的MMA產物
13導引至儲存槽
d(方法步驟d)中,而包含氧之氣體混合物
15流經該儲存槽
d。將較佳包含至少10體積%之氧的包含MMA之氣流
GS4從該儲存槽導出,且較佳具有低於爆炸下限(LEL)之可燃物質含量。氣流
GS4可經由
4b和
12從該方法排出及/或可經由
4a和
5進料至該縮合步驟
f。該純的甲基丙烯酸烷酯產物之產物流
14從該儲存槽d導出。
由方法步驟a、b、c及/或d所得之氣態輸出物流
5,尤其藉由流
GS1/1a 、 GS2/2a 、 GS3/3a及/或
GS4/4a之一或多者所形成者被導至該縮合設備
f中,其中在方法步驟
f中獲得之該縮合物係經由
11a再循環至方法步驟
b及視情況之
c中且視情況地經
11b部分地被排放。
圖3(用於本發明之實例B1的方案)顯示根據本發明之方法的較佳具體例的流程圖。
附帶物質流之方法步驟a、b、c及d對應於以上對於圖2之描述。
由方法步驟a、b、c及/或d所得之氣態輸出物流被導至該吸收步驟e中以作為氣態輸出物流
5,尤其是藉由
GS1/1a 、 GS2/2a 、 GS3/3a及/或
GS4/4a之一或多者所形成者。
在根據圖3的具體例中,該氣態輸出物流
5係進料至該第一吸收步驟e1(甲醇洗滌)中,其中彼係以新鮮的甲醇
6處理。這產生富甲醇且耗盡MMA之氣流
7(其係導至該第二吸收步驟
e2(水洗滌)中),以及負載MMA之吸收劑
11(其係經由
11a再循環至方法步驟
b且視情況地部分再循環至方法步驟
c中,且視情況地經由
11b從該方法部分地排出)。
在該第二吸收步驟
e2中,該耗盡MMA之氣流
7係以新鮮之水
8處理以獲得耗盡MMA和甲醇之廢氣
9,其係從該方法排出且例如送去焚化。另外獲得的是負載甲醇之水性吸收劑
10,其係再循環至該第一吸收步驟
e1中,視情況地經由
10a和
11部分地再循環至方法步驟
b中,且視情況地經由
10b從該方法部分地排放。
圖4(用於本發明實例B2之方案)顯示根據本發明之用於製備MMA之方法的進一步較佳具體例的流程圖,尤其是處理該氣態輸出物流
5,尤其是藉由吸收而由
GS2,
GS3和
GS4所形成者,其中以甲醇吸收MMA和以水吸收甲醇係在設備
e中進行。在該吸收塔
e中,新鮮之甲醇
6係在該氣態輸出物流
5之添加點上方添加且新鮮之水
8係在新鮮之甲醇
6之添加點上方添加。該氣流
5和該液體吸收劑
6和
8較佳係逆流地導引。該耗盡MMA和甲醇之廢氣
9係從該方法排放。該負載MMA和甲醇之吸收劑
11係再循環至方法步驟
b中。
參考符號之列述在圖1中之簡稱及對圖1之描述具有以下意義:
實例比較用實例V1:用於回收MMA之該結合之氣態輸出物流GS1、GS2、GS3及GS4的冷凝
比較用實例V1係關於一種基於根據圖2之流程圖而用於藉由該ACH-磺基方法製備甲基丙烯酸甲酯(MMA)的方法。所得之結果係在表1中詳述。
(a) 醯胺化/轉化
在方法步驟
a中,13 847 kg/h之丙酮氰醇(ACH)
16(其具有99.0%之丙酮氰醇、0.3%之丙酮、0.5%之水的組成)以及分開的硫酸
17以1.63/1 [kg H
2SO
4/kg ACH]之質量比率與99.7%之硫酸被進料至醯胺化/轉化。該醯胺化係在98℃下進行,且該轉化係在158℃及980毫巴(a)之壓力下進行。此外,在該醯胺化/轉化中,藉由副反應所形成之廢氣
GS1係從該液體反應混合物分離且呈物質流
1a形式進料至冷凝
f。該廢氣
GS1或
1a之組成顯示於表1中。
(b) 酯化
在該醯胺化/轉化
a之過程中獲得的該第二反應混合物(其係由甲基丙烯醯胺(MAA)、甲基丙烯酸(MA)及羥基異丁醯胺(HIBAm)構成,溶在硫酸中)則被送至該酯化
b。在不使用再循環流
11下,該第二液體反應混合物係在供應4850 kg/h之甲醇作為流
6;2000 kg/h之水作為流
8及3220 kg/h之在約100-140℃及50-150毫巴(g)之稍微提高的壓力的直接蒸汽下被酯化。
在該酯化
b中所形成之該粗製的MMA產物然後被蒸餾且與來自冷凝
f的再循環流
11a一同被進料以從該熱後處理
c移除MMA。在方法步驟
b中殘留之稀釋廢酸係從該方法(b)排出。
為要抑制聚合物形成,在方法步驟
b中,在不同點上使用苯二胺系之穩定劑的溶液,而為要有最理想功能,需要氧。在方法步驟
b中,為此目的,具有21體積%之氧含量的空氣在數個點上被進料以作為包含氧之氣體混合物
15。
在該酯化
b中,尤其是在
b中該粗製的MMA產物的蒸餾中,獲得氣態輸出物流
GS2。
(c) 熱後處理
MMA從該粗製的MMA產物的分離包含多個熱分離步驟
c及至少二個蒸餾階段,而低沸物餾分係在該第一階段中分離且高沸物餾分係在該第二階段分離,產生該純的MMA產物
13作為來自最後蒸餾步驟的頂部餾分。
在熱後處理
c中,如同在方法步驟
b中者,具有21體積%之O
2含量的空氣被添加以作為呈包含氧之氣體混合物
15形式的穩定劑的輔劑。獲得氣態輸出物流
GS3。
GS2和
GS3之量和組成係在表1中摘述。所得之廢氣的體積係在表1中顯示。
在多個熱方法步驟
c中獲得之該純化的純MMA產物
13後續被冷卻至8℃且進料至儲存槽
d。
(d) 該純的MMA產物的儲存
為使在儲油場
d中之該穩定劑有最理想的功能,具有21體積%之O
2含量的空氣同樣地被進料至該儲油場
d中以作為包含氧之氣體混合物
15。獲得具有根據表1之MMA含量的氣態輸出物流
GS4。此外,連續填充和清空操作所得之另外的MMA飽和的廢氣被添加至該出口流
GS4。該輸出物流
GS4同樣地被進料至該部分冷凝
f中以供用於回收MMA。
GS4之量和組成係在表1中摘述。
(f) 該等氣態輸出物流之冷凝
結合該等氣態輸出物流
GS1、
GS2、
GS3和
GS4以產生結合的方法廢氣
5且送至用於冷凝
f之設備。在約12℃之方法面的溫度水平下進行該冷凝
f。所用之冷媒是在進料溫度約1℃的冷水。來自
5之MMA的氣體冷卻和部分冷凝係在垂直配置之殼管型設備中,在990毫巴(a)之稍微降低的壓力下,在該冷凝
f中逆流地進行。
該冷凝的MMA
11a被連續地送至熱後處理
c,同時該耗盡的廢氣
9被送至後燃燒。
比較用實例V2:冷凝該結合的氣態輸出物流GS2、GS3及GS4以供回收MMA
比較用實例V2係關於一種基於根據圖2之流程圖而藉由該ACH磺基方法製備甲基丙烯酸甲酯(MMA)的方法。所得結果在表1中詳述。
比較用實例V2之實施係根據上述之比較用實例V1。與比較用實例V1對比之下,僅結合該氣態輸出物流
GS2、
GS3和
GS4以產生氣流
5且導引至該冷凝
f中以供回收MMA。
藉由在醯胺化/轉化中的副反應所形成之廢氣
GS1係從該液體反應混合物分離且呈物質流
1c之形式從該方法排出且送去焚化。該廢氣
GS1或
1c之組成係在表1中顯示。
表 1 :比較用實例 V1 和 V2 之比較
a:醯胺化及轉化 b:酯化 c:熱後處理區 d:儲存/儲存槽 e1:第一吸收步驟(甲醇洗滌) e2:第二吸收步驟(水洗滌) e:吸收/結合之甲醇-水洗滌 f:部分冷凝 GS1:來自方法步驟a之包含一氧化碳和二氧化硫之氣流 GS2:來自方法步驟b之包含MMA之氣流(較佳具有<10體積%之氧濃度) GS3:來自方法步驟c之包含MMA之氣流(較佳具有<10體積%之氧濃度) GS4:來自儲存d之包含MMA之氣流(較佳低於爆炸下限LEL) 1a,b,c:來自醯胺化/轉化之廢氣(較佳地<10體積%之O 2) 2a,b:來自酯化之廢氣(包含MMA;較佳地<10體積%之O 2) 3a,b:來自熱後處理之廢氣(包含MMA;較佳地<10體積%之O 2) 4a,b:儲油槽之廢氣(包含MMA;較佳地>10體積%之O 2) 5:用於後處理之氣態輸出物流GS 6:新鮮的甲醇(反應物和視情況之洗滌用液體) 7:來自e1之富甲醇之氣流(耗盡MMA) 8:新鮮的水(反應物和視情況之洗滌用液體) 9:廢氣(耗盡MMA及甲醇) 10,10a,b:負載甲醇之水性吸收劑 11,11a,b:負載MMA之吸收劑(包含水、MMA和甲醇) 12:用於熱後處理之廢氣 13:純的MMA產物 14:來自儲存之該純的MMA產物的產物流 15:包含氧之氣體混合物進料 16:ACH進料 17:硫酸進料 a: Amination and conversion b: Esterification c: Thermal post-treatment area d: Storage/storage tank e1: First absorption step (methanol washing) e2: Second absorption step (water washing) e: Absorbed/combined methanol - water scrubbing f: partial condensation GS1: gas stream from process step a containing carbon monoxide and sulfur dioxide GS2: gas stream from process step b containing MMA (preferably with an oxygen concentration of <10% by volume) GS3: gas stream from process step c Gas stream containing MMA (preferably with an oxygen concentration of <10% by volume) GS4: Gas stream containing MMA from storage d (preferably below the lower explosion limit LEL) 1a, b, c: Waste gas from amination/conversion ( Preferably <10% by volume O 2 ) 2a, b: Waste gas from esterification (including MMA; preferably <10% by volume O 2 ) 3a, b: Waste gas from thermal post-treatment (including MMA; preferably less than 10% by volume) Preferably <10 volume % O 2 ) 4a, b: Waste gas from oil storage tank (including MMA; preferably > 10 volume % O 2 ) 5: Gaseous output stream GS for post-processing 6: Fresh methanol ( Reactants and optional scrubbing liquid) 7: Methanol-rich gas stream from e1 (depleted of MMA) 8: Fresh water (reactants and optional scrubbing liquid) 9: Waste gas (depleted of MMA and methanol) 10,10a,b: Methanol-loaded aqueous absorbent 11,11a,b: MMA-loaded absorbent (including water, MMA and methanol) 12: Waste gas for thermal post-treatment 13: Pure MMA product 14: From storage Product stream of the pure MMA product 15: Gas mixture containing oxygen feed 16: ACH feed 17: Sulfuric acid feed
[圖1]描述從反應性MMA前驅物化合物(其可選擇性地從C2單元乙烯、C3單元丙酮、或C4單元異丁烯製造)形成甲基丙烯酸甲酯的高度廣泛的反應網絡。 [圖2] (用於比較用實例V1和V2之方案)顯示製備MMA之流程圖。 [圖3] (用於發明實例B1之方案)顯示根據本發明之方法的較佳具體例的流程圖。 [圖4] (用於發明實例B2之方案)顯示根據本發明之用於製備MMA之方法的進一步較佳具體例的流程圖。 [Fig. 1] Describes a highly extensive reaction network for the formation of methyl methacrylate from a reactive MMA precursor compound that is selectively manufactured from C2 unit ethylene, C3 unit acetone, or C4 unit isobutylene. [Fig. 2] (Protocol for comparison of Examples V1 and V2) shows a flow chart for preparing MMA. [Fig. 3] (Scheme used in Inventive Example B1) shows a flow chart of a preferred specific example of the method according to the present invention. [Fig. 4] (Scheme for Inventive Example B2) shows a flow chart of a further preferred specific example of the method for preparing MMA according to the present invention.
a:醯胺化及轉化 a: Amidation and transformation
b:酯化 b:Esterification
c:熱後處理區 c:Heat post-treatment area
d:儲存/儲存槽 d:storage/storage tank
e1:第一吸收步驟(甲醇洗滌) e1: First absorption step (methanol washing)
e2:第二吸收步驟(水洗滌) e2: Second absorption step (water washing)
1a,1b,1c:來自醯胺化/轉化之廢氣(較佳地<10體積%之O2) 1a, 1b, 1c: Waste gas from amination/conversion (preferably <10 vol% O 2 )
2a,2b:來自酯化之廢氣(包含MMA;較佳地<10體積%之O2) 2a, 2b: Waste gas from esterification (including MMA; preferably <10 volume % O 2 )
3a,3b:來自熱後處理之廢氣(包含MMA;較佳地<10體積%之O2) 3a, 3b: Waste gas from thermal post-treatment (including MMA; preferably <10 volume % O 2 )
4a,4b:儲油槽之廢氣(包含MMA;較佳地>10體積%之O2) 4a, 4b: Waste gas from oil storage tank (including MMA; preferably >10 volume% O 2 )
GS1:來自方法步驟a之包含一氧化碳和二氧化硫之氣流 GS1: Gas stream containing carbon monoxide and sulfur dioxide from method step a
GS2:來自方法步驟b之包含MMA之氣流(較佳具有<10體積%之氧濃度) GS2: Gas stream containing MMA from method step b (preferably with an oxygen concentration of <10 vol%)
GS3:來自方法步驟c之包含MMA之氣流(較佳具有<10體積%之氧濃度) GS3: Gas stream containing MMA from method step c (preferably with an oxygen concentration of <10 vol%)
GS4:來自儲存d之包含MMA之氣流(較佳低於爆炸下限LEL) GS4: Gas flow containing MMA from storage d (preferably below the lower explosion limit LEL)
5:用於後處理之氣態輸出物流GS 5: Gaseous output logistics GS for post-processing
6:新鮮的甲醇(反應物和視情況之洗滌用液體) 6: Fresh methanol (reactants and washing liquid as appropriate)
7:來自e1之富甲醇之氣流(耗盡MMA) 7: Methanol-rich gas flow from e1 (depleted MMA)
8:新鮮的水(反應物和視情況之洗滌用液體) 8: Fresh water (reactants and washing liquid as appropriate)
9:廢氣(耗盡MMA及甲醇) 9: Exhaust gas (exhaust MMA and methanol)
10,10a,10b:負載甲醇之水性吸收劑 10,10a,10b: Aqueous absorbent loaded with methanol
11,11a,11b:負載MMA之吸收劑(包含水、MMA和甲醇) 11,11a,11b: MMA loaded absorbent (including water, MMA and methanol)
12:用於熱後處理之廢氣 12: Waste gas used for thermal post-treatment
13:純的MMA產物 13: Pure MMA product
14:來自儲存之該純的MMA產物的產物流 14: Product stream from storage of the pure MMA product
15:包含氧之氣體混合物進料 15: Feed of gas mixture containing oxygen
16:ACH進料 16:ACH feed
17:硫酸進料 17: Sulfuric acid feed
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