CN110092358A - A kind of processing method of waste sulfuric acid from alkylation - Google Patents

A kind of processing method of waste sulfuric acid from alkylation Download PDF

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Publication number
CN110092358A
CN110092358A CN201910440175.7A CN201910440175A CN110092358A CN 110092358 A CN110092358 A CN 110092358A CN 201910440175 A CN201910440175 A CN 201910440175A CN 110092358 A CN110092358 A CN 110092358A
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sulfuric acid
alkylation
solvent
waste sulfuric
processing method
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孙伟振
赵玲
刘梦雪
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East China University of Science and Technology
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East China University of Science and Technology
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    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01BNON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
    • C01B17/00Sulfur; Compounds thereof
    • C01B17/69Sulfur trioxide; Sulfuric acid
    • C01B17/90Separation; Purification
    • C01B17/92Recovery from acid tar or the like, e.g. alkylation acids
    • C01B17/925Recovery from acid tar or the like, e.g. alkylation acids by processes involving a liquid-liquid extraction
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/50Improvements relating to the production of bulk chemicals
    • Y02P20/54Improvements relating to the production of bulk chemicals using solvents, e.g. supercritical solvents or ionic liquids

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  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Inorganic Chemistry (AREA)
  • Organic Low-Molecular-Weight Compounds And Preparation Thereof (AREA)

Abstract

The invention discloses a kind of processing methods of waste sulfuric acid from alkylation.The processing method of waste sulfuric acid from alkylation disclosed by the invention is the following steps are included: waste sulfuric acid from alkylation, solvent and ionic liquid are mixed, liquid separation.The processing method of waste sulfuric acid from alkylation of the invention is at low cost, less energy consumption, pollution are small, it can be achieved that Waste Sulfuric Acid regeneration.

Description

A kind of processing method of waste sulfuric acid from alkylation
Technical field
The present invention relates to a kind of processing methods of waste sulfuric acid from alkylation.
Background technique
Alkylate oil can meet the gasoline blend component of cleaning and high-octane rating requirement simultaneously, and alkylation process is to the world Oil product upgrading is significant.Catalyst of the sulfuric acid in reaction zone as alkylated reaction, theoretically, catalyst promote chemistry anti- It answers and itself should not change.But actually due to the influence of the impurity in side reaction and raw material, sour concentration will gradually be dropped Low, a part of acid will be consumed.Optimum acid concentration is probably in 89%-96%, alkylation per ton in sulfuric acid alkylation plant The acid consumption of oil is about between 77-102Kg, then the device of an annual output 100Kt alkylate oil, will consume nearly 10Kt's in 1 year Sulfuric acid, and generate almost same amount of spent acid.
Waste sulfuric acid from alkylation is a kind of biggish dark red colloidal liquid of viscosity, and ingredient is mainly free sulfuric acid, high score Sub- alkene, alkadienes, alkyl sulfonic acid, alkylsurfuric acid and dissolution sulfide (hydrogen sulfide, mercaptan etc.) therein, property are unstable It is fixed, can constantly be oxidized in air, after and the reactions such as olefinic polymerization oxidation can occur, give out off-odor.Largely Spent acid is difficult to handle, it will greatly threatens environment composition.
Currently, the first is by alkyl sulfur both at home and abroad there are mainly three types of industrialized waste sulfuric acid from alkylation treatment process Acid is used to produce ammonium sulfate, fertilizer etc. after concentrating.The ammonium sulfate color that such technical matters is produced is deeper, irritant gas Body generates.Organic matter in the Waste Sulfuric Acid of part enters crops by fertilizer, further endangers human health.Second is to utilize It is alkylated spent acid production white carbon black and petroleum antirust agent.This method wastewater discharge is big, and the added value of product of generation is low.The third is Using high-temperature cracking method, alkylation spent acid is made to be cracked into SO2And H2O, organic cracking is at CO2And H2O, then gas again into Enter regeneration of sulfuric acid device, generates technical grade sulfuric acid.Such method and process is mature, but energy consumption is high for cracking sulfuric acid at high temperature, to setting Standby corrosion is more serious, causes this kind of processing method operating cost high, system investments are big.
Summary of the invention
The technical problem to be solved by the present invention is in order to overcome in the prior art waste sulfuric acid from alkylation processing method it is few Defect, and provide a kind of processing method of waste sulfuric acid from alkylation.This method is at low cost, less energy consumption, pollution are small, it can be achieved that sulfur waste The regeneration of acid.
The present invention mainly solves above-mentioned technical problem by the following technical programs.
The present invention provides a kind of processing methods of waste sulfuric acid from alkylation comprising following steps: by waste sulfuric acid from alkylation, Solvent and ionic liquid mixing, liquid separation.
The solvent can be conventional for this field, and specifically preferred according to the invention is alkane solvents, aromatic hydrocarbon solvent, alkyl halide One of hydrocarbon solvent and ether solvent are a variety of, further preferably alkane solvents, aromatic hydrocarbon solvent and halogenated alkane One of class solvent is a variety of.The alkane solvents can be conventional for this field, and specifically preferred according to the invention is propane, positive fourth One of alkane, iso-butane and n-hexane are a variety of, further preferably iso-butane.The aromatic hydrocarbon solvent can be this field Conventional, specifically preferred according to the invention is benzene and/or toluene, further preferably toluene.The halogenated alkanes solvents can be this Field is conventional, specifically preferred according to the invention for one of methylene chloride, chloroform and carbon tetrachloride or a variety of.The ether solvent Can be conventional for this field, specifically preferred according to the invention is tetrahydrofuran.
Cation in the ionic liquid be preferably alkyl imidazolium cation, pyrazoles cationoid, pyridine cationoid, One of pyrroles's cationoid, morphine cationoid, quaternaries cation and quaternary alkylphosphonium salt cationoid are a variety of, further Preferably alkyl imidazolium cation.
The alkyl imidazolium cation can be conventional for this field, and the present invention is preferably 1-C1~C10Alkyl -3-C1~C10Alkane Base glyoxaline cation, further preferably 1-C4~C8Alkyl -3-C1~C4Alkylimidazolium cation is still more preferably 1- One in butyl -3- methyl imidazolium cation, 1- hexyl -3- methyl imidazolium cation and 1- octyl -3- methyl imidazolium cation Kind is a variety of.
Anion in the ionic liquid is preferably Br-、Cl-、BF4 -、PF6 -、NTf2 -、C(CN)3 -、N(CN)2 -With [CH3(C2H4O)2SO4]-(i.e.) one of or a variety of, further preferably PF6 -、BF4 -With NTf2 -One of or it is a variety of.
The ionic liquid is preferably 1- butyl -3- methylimidazole hexafluorophosphate, 1- hexyl -3- methylimidazole hexafluoro Phosphate, 1- octyl -3- methylimidazole hexafluorophosphate, 1- butyl -3- methyl imidazolium tetrafluoroborate, 1- hexyl -3- methyl Tetrafluoroborate, 1- octyl -3- methyl imidazolium tetrafluoroborate, 1- butyl -3- methylimidazole bis-trifluoromethylsulfoandimide In salt, 1- hexyl -3- methylimidazole bis-trifluoromethylsulfoandimide salt and 1- octyl -3- methylimidazole bis-trifluoromethylsulfoandimide salt One or more, further preferably 1- butyl -3- methylimidazole bis-trifluoromethylsulfoandimide salt, 1- butyl -3- methyl miaow One of azoles hexafluorophosphate, 1- butyl -3- methylimidazole hexafluorophosphate and 1- hexyl -3- methyl imidazolium tetrafluoroborate Or it is a variety of.
The mass ratio of the solvent and the waste sulfuric acid from alkylation is preferably 0.1:1~15:1, further preferably 0.5:1~10:1 is still more preferably 2:1~10:1 (such as 2:1,5:1 and 10:1).
The mass ratio of the ionic liquid and the waste sulfuric acid from alkylation is preferably 0.1:1~5:1, further preferably For 0.4:1~2:1, further preferably 1:1~2:1 (such as 1:1 and 2:1).
The mixed mode can be conventional for this field, specifically preferred according to the invention for stirring, further preferably machinery Stirring.The churned mechanically revolving speed is preferably 100~2000r/min, further preferably 500~1500r/min (such as 500r/min, 1000r/min and 1500r/min).
The mixed temperature can be conventional for this field, and specifically preferred according to the invention is 0~80 DEG C, further preferably 5 ~60 DEG C, be still more preferably 10~30 DEG C (such as 25 DEG C and 30 DEG C).
The mixed time can be conventional for this field, specifically preferred according to the invention for more than or equal to 5 minutes, further excellent Be selected as 5 minutes~3 hours, still more preferably for 0.5~3 hour (such as 0.5 hour, 0.75 hour, 1 hour, 1.5 hours, 3 hours).
The mixed pressure can be conventional for this field, and specifically preferred according to the invention is 0.1~2MPa, further preferably 0.1~0.4MPa (such as 0.1MPa and 0.4MPa).
The mode of the liquid separation can be conventional for this field, specifically preferred according to the invention to stand or being centrifuged, further preferably For centrifugation.
The temperature of the liquid separation can be conventional for this field, those skilled in the art can by the solvent type into Row adjustment, specifically preferred according to the invention is 0~80 DEG C, and further preferably 5~60 DEG C, be still more preferably 10~30 DEG C of (examples Such as 25 DEG C).
It can also further comprise the recycling of ionic liquid after the liquid separation.The mode of the recycling is preferably by liquid separation The supernatant liquid obtained afterwards is evaporated under reduced pressure.
In the present invention, the waste sulfuric acid from alkylation is preferably that alkylated reaction occurs in concentrated sulfuric acid for butylene and iso-butane Generated Waste Sulfuric Acid.The waste sulfuric acid from alkylation is preferably the waste sulfuric acid from alkylation from the Zhejiang match chromium energy.
In actual alkyl chemical industry, black sulfuric acid and fresh sulfuric acid (mass concentration 98%-99%) enter alkane together In glycosylation reaction device, the molten hydrocarbon of acid of remaining height ionization is diluted, and just be can be used as proton transfer medium, is promoted alkyl Change the generation of main reaction.
Without prejudice to the field on the basis of common sense, above-mentioned each optimum condition, can any combination to get the present invention it is each preferably Example.
The reagents and materials used in the present invention are commercially available.
The positive effect of the present invention is that: the present invention extracts the molten hydrocarbon of acid in waste sulfuric acid from alkylation using extraction, Mechanical stirring comes into full contact with Waste Sulfuric Acid and organic solvent, and the impurity in spent acid is dissolved in solvent.Compared with high-temperature cracking method, Apparatus cost is small, and low energy consumption, is that can carry out industrialized method.Select ionic liquid as extraction process extractant, Its physicochemical properties changes with the variation of ionic liquid zwitterion type and substituent group, has very extensive dissolution energy Power and for target substance have can modulation soluble end, dissolubility of the molten hydrocarbon of acid in extractant can be enhanced.Ion simultaneously Liquid has lower saturated vapor pressure and more stable thermodynamic property, can recycle in extraction process, reduces loss, And then it reduces environmental pollution.
Specific embodiment
The present invention is further illustrated below by the mode of embodiment, but does not therefore limit the present invention to the reality It applies among a range.In the following examples, the experimental methods for specific conditions are not specified, according to conventional methods and conditions, or according to quotient The selection of product specification.
What the molten hydrocarbon of acid was primarily referred to as being formed in alkylated reaction in the present invention contains a large amount of double bond conjugated dienes, C5Ring And its hydrocarbon polymer (the C of branched chain compound12-C20)。
Extraction efficiency=[(C in the present invention0-Cf)/C0] * 100%, wherein C0Refer to extracting the molten hydrocarbon of acid in preceding spent acid Concentration;CfFor the concentration of the molten hydrocarbon of acid in spent acid after extraction.The volume of spent acid and spent acid after extraction is basically unchanged before extracting.The present invention Waste sulfuric acid from alkylation refers to that butylene and iso-butane are alkylated in concentrated sulfuric acid in following Examples 1 to 4 and comparative example 1 Waste Sulfuric Acid caused by reacting, waste sulfuric acid from alkylation of the Waste Sulfuric Acid from the Zhejiang match chromium energy.Utilize ultraviolet specrophotometer The absorbance for measuring the organic compound containing conjugated double bond structures carries out quantitative analysis to the molten hydrocarbon component content of acid.
Embodiment 1
Conical flask is added in the 1- butyl -3- methylimidazole hexafluorophosphate of 10g waste sulfuric acid from alkylation, 20g toluene, 10g In 250mL, 1h is mixed under conditions of 25 DEG C, 0.1MPa, power of agitator 1000r/min.It is mixed by what is obtained after stirring Liquid pouring is closed in centrifuge tube, carries out Liquid liquid Separation using centrifuge at 25 DEG C.After the completion of centrifugation, supernatant liquid is containing quilt Extract the extraction phase of the molten hydrocarbon of object acid, toluene and 1- butyl -3- methylimidazole hexafluorophosphate, lower layer is black sulfuric acid extracted Phase.Toluene and the molten hydrocarbon of acid can be separated through vacuum distillation, toluene and 1- butyl -3- methylimidazole hexafluorophosphate can be recycled. The single extraction efficiency of the molten hydrocarbon of acid is 81.2%.
Embodiment 2
By 10g waste sulfuric acid from alkylation, 50g methylene chloride, 10g (1- butyl -3- methylimidazole hexafluorophosphate and 1- oneself Base -3- methyl imidazolium tetrafluoroborate) (wherein 1- butyl -3- methylimidazole hexafluorophosphate and 1- hexyl -3- methylimidazole four The molar ratio of borofluoride is 1:1) it is added in conical flask 250mL, under conditions of 30 DEG C, 0.1MPa, power of agitator 500r/min 1.5h is mixed.After stirring, obtained mixed liquor is stood at 25 DEG C and carries out Liquid liquid Separation.Supernatant liquid is containing quilt Extract the molten hydrocarbon of object acid, methylene chloride, 1- butyl -3- methylimidazole hexafluorophosphate and 1- hexyl -3- methyl imidazolium tetrafluoroborate Extraction phase, lower layer be black sulfuric acid phase extracted.Methylene chloride and the molten hydrocarbon of acid can be separated by being evaporated under reduced pressure, methylene chloride, 1- butyl -3- methylimidazole hexafluorophosphate and 1- hexyl -3- methyl imidazolium tetrafluoroborate can be recycled.The list of the molten hydrocarbon of acid Secondary extraction efficiency is 86.1%.
Embodiment 3
By 5g waste sulfuric acid from alkylation, 50g iso-butane, 5g (1- butyl -3- methylimidazole bis-trifluoromethylsulfoandimide salt and 1- butyl -3- methylimidazole hexafluorophosphate) (wherein 1- butyl -3- methylimidazole bis-trifluoromethylsulfoandimide salt and 1- butyl - The molar ratio of 3- methylimidazole hexafluorophosphate is 1:1) it is added in conical flask 250mL, 25 DEG C, 0.4MPa, power of agitator 0.5h is mixed under conditions of 1500r/min.After stirring, obtained mixing liquid is poured in centrifuge tube, 25 Liquid liquid Separation is carried out using centrifuge at DEG C.After the completion of centrifugation, supernatant liquid is containing by the molten hydrocarbon of extraction object acid, iso-butane, 1- butyl- The extraction phase of 3- methylimidazole bis-trifluoromethylsulfoandimide salt and 1- butyl -3- methylimidazole hexafluorophosphate, lower layer are extraction Black sulfuric acid phase afterwards.1- butyl -3- methylimidazole bis-trifluoromethylsulfoandimide salt and 1- butyl -3- can be separated through vacuum distillation Methylimidazole hexafluorophosphate and the molten hydrocarbon of acid, 1- butyl -3- methylimidazole bis-trifluoromethylsulfoandimide salt and 1- butyl -3- methyl Limidazolium hexafluorophosphate can be recycled.The single extraction efficiency of the molten hydrocarbon of acid is 88.8%.
Embodiment 4
By 5g waste sulfuric acid from alkylation, 25g iso-butane, 5g (1- butyl -3- methylimidazole hexafluorophosphate and 1- hexyl - 3- methyl imidazolium tetrafluoroborate) (wherein 1- butyl -3- methylimidazole hexafluorophosphate and 1- hexyl -3- methylimidazole tetrafluoro The molar ratio of borate is 1:1) it is added in conical flask 250mL, 30 DEG C, it is mixed under conditions of 0.4MPa, 1000r/min. After stirring, obtained mixing liquid is poured in centrifuge tube, carries out Liquid liquid Separation using centrifuge.After the completion of centrifugation, Supernatant liquid is containing by the molten hydrocarbon of extraction object acid, iso-butane, 1- butyl -3- methylimidazole hexafluorophosphate and 1- hexyl -3- methyl miaow The extraction phase of azoles tetrafluoroborate, lower layer are black sulfuric acid phase extracted.1- butyl -3- methyl miaow can be separated through vacuum distillation Azoles hexafluorophosphate and 1- hexyl -3- methyl imidazolium tetrafluoroborate and the molten hydrocarbon of acid, 1- butyl -3- methylimidazole hexafluorophosphate It can be recycled with 1- hexyl -3- methyl imidazolium tetrafluoroborate.The single extraction efficiency of the molten hydrocarbon of acid is as shown in table 1.
The single extraction efficiency of the molten hydrocarbon of acid under the different extraction times of table 1
Comparative example 1
10g waste sulfuric acid from alkylation and 20g toluene are added in 250mL conical flask, 25 DEG C, 0.1MPa, power of agitator 1h is mixed under conditions of 1000r/min.After stirring, obtained mixing liquid is poured in centrifuge tube, at 25 DEG C It is lower to carry out Liquid liquid Separation using centrifuge.After the completion of centrifugation, supernatant liquid is toluene phase, and lower layer is sulfuric acid phase extracted.It should The toluene that process obtains mutually without apparent color change, does not contain the chromatographic peak of the molten hydrocarbon of acid mutually through gas chromatographic analysis toluene.

Claims (10)

1. a kind of processing method of waste sulfuric acid from alkylation, which is characterized in that it is the following steps are included: by waste sulfuric acid from alkylation, molten Agent and ionic liquid mixing, liquid separation.
2. the processing method of waste sulfuric acid from alkylation as described in claim 1, which is characterized in that
The solvent is one of alkane solvents, aromatic hydrocarbon solvent, halogenated alkanes solvents and ether solvent or a variety of;
And/or the cation in the ionic liquid is alkyl imidazolium cation, pyrazoles cationoid, pyridine cationoid, pyrrole Cough up one of cationoid, morphine cationoid, quaternaries cation and quaternary alkylphosphonium salt cationoid or a variety of;
And/or the anion in the ionic liquid is Br-、Cl-、BF4 -、PF6 -、NTf2 -、C(CN)3 -、N(CN)2 -[CH3 (C2H4O)2SO4]-One of or it is a variety of;
And/or the mass ratio of the solvent and the waste sulfuric acid from alkylation is 0.1:1~15:1;
And/or the mass ratio of the ionic liquid and the waste sulfuric acid from alkylation is 0.1:1~5:1;
And/or the mixed mode is stirring;
And/or the mixed temperature is 0~80 DEG C;
And/or the mixed time is more than or equal to 5 minutes;
And/or the mixed pressure is 0.1~2MPa;
And/or the mode of the liquid separation is to stand or be centrifuged;
And/or the temperature of the liquid separation is 0~80 DEG C.
3. the processing method of waste sulfuric acid from alkylation as claimed in claim 2, which is characterized in that
When the solvent is alkane solvents, the solvent is one of propane, normal butane, iso-butane and n-hexane Or it is a variety of;
And/or when the solvent is aromatic hydrocarbon solvent, the solvent is benzene and/or toluene;
And/or when the solvent is halogenated alkanes solvents, the solvent is methylene chloride, chloroform and carbon tetrachloride One of or it is a variety of;
And/or when the solvent is ether solvent, the solvent is tetrahydrofuran;
And/or the cation in the ionic liquid is alkyl imidazolium cation;
And/or the anion in the ionic liquid is PF6 -、BF4 -And NTf2 -One of or it is a variety of;
And/or the mass ratio of the solvent and the waste sulfuric acid from alkylation is 0.5:1~10:1;
And/or the mass ratio of the ionic liquid and the waste sulfuric acid from alkylation is 0.4:1~2:1;
And/or the mixed mode is mechanical stirring;
And/or the mixed temperature is 5~60 DEG C;
And/or the mixed time is 5 minutes~3 hours;
And/or the mixed pressure is 0.1~0.4MPa;
And/or the mode of the liquid separation is centrifugation;
And/or the temperature of the liquid separation is 5~60 DEG C.
4. the processing method of waste sulfuric acid from alkylation as claimed in claim 3, which is characterized in that
When the solvent is alkane solvents, the solvent is iso-butane;
And/or when the solvent is aromatic hydrocarbon solvent, the solvent is toluene;
And/or the alkyl imidazolium cation is 1-C1~C10Alkyl -3-C1~C10Alkylimidazolium cation;
And/or the mass ratio of the solvent and the waste sulfuric acid from alkylation is 2:1~10:1;
And/or the mass ratio of the ionic liquid and the waste sulfuric acid from alkylation is 1:1~2:1;
And/or the churned mechanically revolving speed is 100~2000r/min;
And/or the mixed temperature is 10~30 DEG C;
And/or the mixed time is 0.5~3 hour;
And/or the temperature of the liquid separation is 10~30 DEG C.
5. the processing method of waste sulfuric acid from alkylation as claimed in claim 4, which is characterized in that
The alkyl imidazolium cation is 1-C4~C8Alkyl -3-C1~C4Alkylimidazolium cation;
And/or the churned mechanically revolving speed is 500~1500r/min.
6. the processing method of waste sulfuric acid from alkylation as claimed in claim 5, which is characterized in that
The alkyl imidazolium cation is that 1- butyl -3- methyl imidazolium cation, 1- hexyl -3- methyl imidazolium cation and 1- are pungent One of base -3- methyl imidazolium cation is a variety of.
7. the processing method of waste sulfuric acid from alkylation as described in claim 1, which is characterized in that the ionic liquid is 1- fourth Base -3- methylimidazole hexafluorophosphate, 1- hexyl -3- methylimidazole hexafluorophosphate, 1- octyl -3- methylimidazole hexafluorophosphoric acid Salt, 1- butyl -3- methyl imidazolium tetrafluoroborate, 1- hexyl -3- methyl imidazolium tetrafluoroborate, 1- octyl -3- methylimidazole The double trifluoro methylsulfonyls of tetrafluoroborate, 1- butyl -3- methylimidazole bis-trifluoromethylsulfoandimide salt, 1- hexyl -3- methylimidazole One of inferior amine salt and 1- octyl -3- methylimidazole bis-trifluoromethylsulfoandimide salt are a variety of.
8. the processing method of waste sulfuric acid from alkylation as claimed in claim 7, which is characterized in that the ionic liquid is 1- fourth Base -3- methylimidazole bis-trifluoromethylsulfoandimide salt, 1- butyl -3- methylimidazole hexafluorophosphate, 1- butyl -3- methylimidazole One of hexafluorophosphate and 1- hexyl -3- methyl imidazolium tetrafluoroborate are a variety of.
9. the processing method of waste sulfuric acid from alkylation as described in any one of claims 1 to 8, which is characterized in that after liquid separation also into One step includes the recycling of the ionic liquid.
10. the processing method of waste sulfuric acid from alkylation as claimed in claim 9, which is characterized in that the mode of the recycling is The supernatant liquid obtained after liquid separation is evaporated under reduced pressure.
CN201910440175.7A 2019-05-24 2019-05-24 A kind of processing method of waste sulfuric acid from alkylation Pending CN110092358A (en)

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111302359A (en) * 2020-03-13 2020-06-19 云南云天化石化有限公司 Method for preparing ammonium sulfate from alkylation waste acid by one-step impurity removal

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
BE788621A (en) * 1972-09-08 1973-03-08 Texaco Development Corp Removing hydrocarbons from spent sulphuric acid catalyst - which has been used for alkylation of olefins or aromatics
DE2247115A1 (en) * 1972-09-26 1974-03-28 Texaco Development Corp Removing hydrocarbons from spent sulphuric acid catalyst - which has been used for alkylation of olefins or aromatics
CN1072905A (en) * 1991-12-02 1993-06-09 赫彻斯特股份公司 The method of separation of organic phosphorous compound and other impurity from dilute sulphuric acid
CN104760938A (en) * 2015-03-18 2015-07-08 安庆师范学院 Method for removing iron ions from concentrated sulfuric acid
CN107754850A (en) * 2016-08-17 2018-03-06 中国科学院过程工程研究所 A kind of method for preparing charcoal base acid material using the alkylation spent acid containing ionic liquid
CN109395776A (en) * 2017-08-17 2019-03-01 华东理工大学 A kind of alkylated reaction catalyst system and its preparation method and application

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
BE788621A (en) * 1972-09-08 1973-03-08 Texaco Development Corp Removing hydrocarbons from spent sulphuric acid catalyst - which has been used for alkylation of olefins or aromatics
DE2247115A1 (en) * 1972-09-26 1974-03-28 Texaco Development Corp Removing hydrocarbons from spent sulphuric acid catalyst - which has been used for alkylation of olefins or aromatics
CN1072905A (en) * 1991-12-02 1993-06-09 赫彻斯特股份公司 The method of separation of organic phosphorous compound and other impurity from dilute sulphuric acid
CN104760938A (en) * 2015-03-18 2015-07-08 安庆师范学院 Method for removing iron ions from concentrated sulfuric acid
CN107754850A (en) * 2016-08-17 2018-03-06 中国科学院过程工程研究所 A kind of method for preparing charcoal base acid material using the alkylation spent acid containing ionic liquid
CN109395776A (en) * 2017-08-17 2019-03-01 华东理工大学 A kind of alkylated reaction catalyst system and its preparation method and application

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
王焕英: "疏水性离子液体萃取再生烷基化废酸", 中国优秀硕士学位论文全文数据库, no. 08, pages 41 - 50 *
马承恕: "染料工业三废治理技术", vol. 1988, 中国化工学会染料学会染料行业环保科技情报网, pages: 179 *

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111302359A (en) * 2020-03-13 2020-06-19 云南云天化石化有限公司 Method for preparing ammonium sulfate from alkylation waste acid by one-step impurity removal

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Application publication date: 20190806