CN117417394A - Method for recycling fructose from 5-hydroxymethylfurfural wastewater - Google Patents

Method for recycling fructose from 5-hydroxymethylfurfural wastewater Download PDF

Info

Publication number
CN117417394A
CN117417394A CN202311429396.7A CN202311429396A CN117417394A CN 117417394 A CN117417394 A CN 117417394A CN 202311429396 A CN202311429396 A CN 202311429396A CN 117417394 A CN117417394 A CN 117417394A
Authority
CN
China
Prior art keywords
fructose
calcium
acid
wastewater
reaction
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
CN202311429396.7A
Other languages
Chinese (zh)
Inventor
王博
梁越
张宇
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Zhongke Guosheng Hangzhou Technology Co ltd
Original Assignee
Zhongke Guosheng Hangzhou Technology Co ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Zhongke Guosheng Hangzhou Technology Co ltd filed Critical Zhongke Guosheng Hangzhou Technology Co ltd
Priority to CN202311429396.7A priority Critical patent/CN117417394A/en
Publication of CN117417394A publication Critical patent/CN117417394A/en
Pending legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C07ORGANIC CHEMISTRY
    • C07HSUGARS; DERIVATIVES THEREOF; NUCLEOSIDES; NUCLEOTIDES; NUCLEIC ACIDS
    • C07H3/00Compounds containing only hydrogen atoms and saccharide radicals having only carbon, hydrogen, and oxygen atoms
    • C07H3/02Monosaccharides
    • CCHEMISTRY; METALLURGY
    • C07ORGANIC CHEMISTRY
    • C07HSUGARS; DERIVATIVES THEREOF; NUCLEOSIDES; NUCLEOTIDES; NUCLEIC ACIDS
    • C07H1/00Processes for the preparation of sugar derivatives
    • C07H1/06Separation; Purification

Landscapes

  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Health & Medical Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Biochemistry (AREA)
  • Biotechnology (AREA)
  • General Health & Medical Sciences (AREA)
  • Genetics & Genomics (AREA)
  • Molecular Biology (AREA)
  • Saccharide Compounds (AREA)

Abstract

The invention belongs to the technical field of biomass wastewater utilization, and particularly relates to a method for recycling fructose from 5-Hydroxymethylfurfural (HMF) wastewater. In order to solve the problem of the current recovery of HMF waste water fructose: the invention mixes the waste water and calcium source in the solvent, the sediment obtained by filtering is washed by weak acid, the filtrate is concentrated and crystallized after passing through the ion exchange column, and the fructose with high purity and high yield is obtained. The used calcium source is common inorganic salt, is green and pollution-free, can utilize various different solvents to regulate and control the reaction, improves the selectivity of fructose recovery, and can realize recycling by further processing, separating and purifying the solvent and the calcium source.

Description

Method for recycling fructose from 5-hydroxymethylfurfural wastewater
Technical Field
The invention relates to the technical field of biomass wastewater utilization, in particular to a method for recycling fructose from 5-Hydroxymethylfurfural (HMF) wastewater.
Background
As a natural food additive, fructose has the advantages of good taste, high sweetness and low calorific value, and is widely applied to important fields such as food, medicine and the like. Meanwhile, due to the specificity of the chemical structure, fructose is also an important raw material for producing 5-Hydroxymethylfurfural (HMF), and HMF is an important platform compound for producing alternative biomass chemical products, so that the method has wide application prospect.
The preparation system of the HMF at the present stage is mainly divided into a water phase system and an organic phase system, but the problems of incomplete reaction, low product purity, difficult separation and the like exist at present, so that a certain amount of fructose which is not completely reacted exists in the waste water of the HMF. The existing recovery method of fructose in wastewater is mainly characterized in that inorganic salt represented by lime milk is added for calcification recovery, the method needs low-temperature operation and strict control of solution pH, the reaction condition is harsh, the fructose yield is low, and the quality of the prepared fructose is difficult to reach the standard of biochemical reagents and is difficult to realize on a large scale.
Therefore, if an industrialized fructose recovery method with controllable temperature, mild reaction conditions, simple and convenient operation and easy grasp can be developed, a new solution is developed for the efficient utilization of HMF wastewater.
Disclosure of Invention
In order to solve the problem of the current recovery of HMF waste water fructose: the invention provides a method for recycling fructose from 5-Hydroxymethylfurfural (HMF) wastewater, which is characterized in that wastewater and a calcium source are mixed in a solvent for reaction, and the fructose is recycled through ion replacement and evaporation concentration.
In order to achieve the purpose of the invention, the technical scheme of the invention is as follows:
in a first aspect, the invention provides a method for recycling fructose from 5-Hydroxymethylfurfural (HMF) wastewater, which comprises the steps of mixing wastewater and calcium sources in a solvent, washing a filtered precipitate by weak acid, and concentrating and crystallizing the filtrate after passing through an ion exchange column to obtain high-purity and high-yield fructose. The method comprises the following steps:
step 1, mixing the wastewater and a calcium source to obtain a mixed solution.
And 2, adding a solvent into the mixed solution obtained in the step 1, and washing the obtained precipitate by using weak acid.
And 3, passing the washing liquid obtained in the step 2 through an ion exchange column, and evaporating and concentrating the obtained washing liquid and the exchange liquid to obtain fructose.
The invention mixes the waste water and the calcium source in the solvent, the sediment obtained by filtering is washed by weak acid, and the filtrate is concentrated and crystallized after passing through the ion exchange column, thus obtaining the fructose with high purity and high yield. The used calcium source is common inorganic salt, is green and pollution-free, can utilize various different solvents to regulate and control the reaction, improves the selectivity of fructose recovery, and can realize recycling by further processing, separating and purifying the solvent and the calcium source.
Further, the calcium source in the step 1 is one of calcium chloride, calcium phosphate, calcium sulfate, calcium acetate, calcium hydrophosphate, calcium biphosphate and calcium carbonate or a mixture of the calcium phosphate, the calcium biphosphate and the calcium carbonate.
Further, the solvent in the step 2 is one or more mixed solvents of methanol, ethanol, ethylene glycol, isopropanol, propylene glycol, glycerol, butanediol, ethylenediamine, ethanolamine, diethyl ether, acetylacetone, N-dimethylformamide and N, N-dimethylacetamide according to any proportion.
Preferably, the molar ratio of the calcium ions in the wastewater and the calcium source in the step 1 is as follows: 1:0.5-20.
Preferably, the reaction temperature in the step 1 is 10-100 ℃ and the reaction time is 5 min-24 h.
Preferably, the weak acid in the step 2 specifically includes at least one of carbonic acid, acetic acid, silicic acid, nitrous acid, hydrogen sulfate, hypochlorous acid, sulfurous acid, and phosphoric acid.
Further preferably, the pH of the mixed solution in the step 2 is 4-7.
Further, the specific steps of ion exchange and recovery of crystalline fructose in the step 3 are as follows:
(1) The filtrate obtained in step 2 is exchanged by a 732 type cation exchange resin and/or a 704 type weak base resin.
(2) Collecting the washing liquid and the exchange liquid, concentrating by a thin film evaporator until no water is distilled out, adding equal amount of methanol for dissolution, decoloring and filtering by active carbon.
(3) Adding a small amount of fructose seed crystal, stirring and crystallizing.
The raw materials or the reagents involved in the invention are all common commercial products, and the related operations are all routine operations in the field unless specified.
The above-mentioned preferable conditions can be combined with each other to obtain a specific embodiment on the basis of common knowledge in the art.
Compared with the prior art, the invention has the following advantages:
(1) Improves the yield and the utilization rate of the fructose.
(2) Can separate and purify fructose from wastewater to obtain fructose products with high yield.
(3) The reaction condition is simple and the operation is controllable.
Drawings
FIG. 1 is a chromatogram of fructose content prior to treatment in example 1;
FIG. 2 is a chromatogram of fructose content after treatment in example 1.
Detailed Description
In order that the above objects, features and advantages of the invention will be more clearly understood, a further description of the invention will be made. It should be noted that, without conflict, the embodiments of the present invention and features in the embodiments may be combined with each other.
In the following description, numerous specific details are set forth in order to provide a thorough understanding of the present invention, but the present invention may be practiced otherwise than as described herein; it will be apparent that the embodiments in the specification are only some, but not all, embodiments of the invention.
Preferred embodiments of the present invention will be described in detail below with reference to examples. It is to be understood that the following examples are given for illustrative purposes only and are not intended to limit the scope of the present invention. Various modifications and alterations of this invention may be made by those skilled in the art without departing from the spirit and scope of this invention.
The experimental methods used in the following examples are conventional methods unless otherwise specified.
Materials, reagents and the like used in the examples described below are commercially available unless otherwise specified.
The percentages appearing in the examples below are percentages by mass unless otherwise indicated.
In the embodiment of the invention, a Waters 2695 liquid chromatograph is adopted for fructose content detection.
Example 1
Preparing a fructose aqueous solution with the mass fraction of 70%, adding an appropriate amount of acid catalyst, taking acetone as an organic solvent, reacting for 1h at 130 ℃ in a multifunctional reaction kettle to obtain a primary reaction solution, removing the organic solvent by rotary evaporation, using water phase wastewater containing fructose obtained after extraction by ethyl acetate, weighing 100g of wastewater to be treated containing fructose, and adding 11.95g of CaCl 2 Stirring and mixing to obtain fructose-CaCl 2 After the double salt is reacted for 3 hours at 25 ℃, adding 100g of excessive ethanol and solution for mixing, fully reacting, standing and filtering to obtain double salt precipitate; dissolving the precipitate in 500mL of 10% by mass of carbonic acid aqueous solution, wherein the pH of the mixed solution is 5.5, filtering, exchanging the filtrate by 732 type cation exchange resin, collecting washing liquid and exchange liquid, concentrating by a thin film evaporator until no water is distilled out, adding equal amount of methanol for dissolving, adding 1% of active carbon for decoloring and filtering, adding a small amount of fructose crystal seeds for stirring and crystallizing, and obtaining crude fructose with the yield of 52.8%.
Example 1 the chromatograms of fructose content before and after treatment are shown in figures 1 and 2.
Example 2
The source of waste water is the same as that of example 1, 100g of waste water to be treated with fructose content of 22.17% is weighed in a 500mL beaker, calcium acetate is added according to the molar ratio of fructose to calcium ions of 1:1, the reaction is carried out for 1h at 25 ℃, 100g of isopropanol is gradually added after the reaction is completed, the reaction is carried out for layering fully, the double salt precipitate obtained by filtration is dissolved in the mixed solution of acetic acid, the pH value of the mixed solution is 5.1, twice distilled water is utilized to carry out ion exchange on the filtrate obtained by filtration through 704 weak base resin, washing liquid and exchange liquid are collected, evaporated and concentrated, after 1% active carbon is decolorized, a small amount of fructose crystal seeds are added for crystallization, and the final crude fructose is obtained, and the yield is 40.54%.
Example 3
The waste water source was the same as in example 1, and waste water, calcium phosphate and sodium chloride were weighed according to a molar ratio of fructose to calcium ions in the waste water of 1:3, with the mass of 100g, 50.12g and 5.9g, respectively. The reaction temperature is between 10 and 20 ℃ and the reaction time is 2 hours. After the reaction is finished, adding a mixed solution of methanol and glycol, filtering after the full reaction is finished, dissolving the obtained precipitate in a mixed solution of hypochlorous acid and acetic acid, wherein the pH value of the mixed solution is 5.7, exchanging the filtrate by 732 type cation exchange resin and 704 type weak base resin, collecting washing liquid and exchange liquid, concentrating by a thin film evaporator until no water is evaporated, adding equal amount of methanol for dissolving, decoloring and filtering by active carbon, and crystallizing the filtrate to obtain crude fructose with the yield of 48.99 percent.

Claims (8)

1. The method for recycling the fructose from the 5-hydroxymethylfurfural wastewater is characterized by comprising the following steps of:
step 1: mixing waste water and a calcium source in the production of the 5-hydroxymethylfurfural containing fructose for reaction to obtain a mixed solution;
step 2: adding a solvent into the mixed solution obtained in the step 1, and dissolving the precipitate obtained after the full reaction by weak acid to obtain a washing solution;
step 3: and (3) carrying out ion exchange and recovery crystallization on the washing liquid obtained in the step (2) to obtain fructose.
2. The method according to claim 1, wherein in step 1, the calcium source is one of calcium chloride, calcium phosphate, calcium sulfate, calcium acetate, calcium hydrogen phosphate, calcium dihydrogen phosphate, calcium carbonate or a mixture with sodium chloride and potassium chloride.
3. The method according to claim 1, wherein in the step 1, the molar ratio of fructose in the wastewater to calcium ions in the calcium source is 1:0.5 to 20.
4. The method according to claim 1, wherein in the step 1, the temperature of the mixing reaction is 10 to 100 ℃, and the time of the mixing reaction is 5min to 24h.
5. The method according to claim 1, wherein in the step 2, the solvent is one or more mixed solvents selected from methanol, ethanol, ethylene glycol, isopropanol, propylene glycol, glycerol, butanediol, ethylenediamine, ethanolamine, diethyl ether, acetylacetone, N-dimethylformamide and N, N-dimethylacetamide according to any proportion.
6. The method according to claim 1, wherein in step 2, the weak acid is at least one of carbonic acid, acetic acid, silicic acid, nitrous acid, hydrogen sulfuric acid, hypochlorous acid, sulfurous acid, and phosphoric acid.
7. The method according to claim 1, wherein in step 2, the pH of the mixture is 4-7.
8. The method according to claim 1, wherein in step 3, the ion exchange and recovery crystallization, in particular, comprises:
(1) Exchanging the washing liquid obtained in the step 2 by 732 type cation exchange resin and/or 704 type weak base resin;
(2) Collecting washing liquid and exchange liquid, concentrating by a thin film evaporator until no water is distilled out, adding methanol for dissolving, decolorizing with active carbon, and filtering;
(3) Adding fructose seed crystal, stirring and crystallizing.
CN202311429396.7A 2023-10-31 2023-10-31 Method for recycling fructose from 5-hydroxymethylfurfural wastewater Pending CN117417394A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202311429396.7A CN117417394A (en) 2023-10-31 2023-10-31 Method for recycling fructose from 5-hydroxymethylfurfural wastewater

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202311429396.7A CN117417394A (en) 2023-10-31 2023-10-31 Method for recycling fructose from 5-hydroxymethylfurfural wastewater

Publications (1)

Publication Number Publication Date
CN117417394A true CN117417394A (en) 2024-01-19

Family

ID=89526171

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202311429396.7A Pending CN117417394A (en) 2023-10-31 2023-10-31 Method for recycling fructose from 5-hydroxymethylfurfural wastewater

Country Status (1)

Country Link
CN (1) CN117417394A (en)

Similar Documents

Publication Publication Date Title
CN102775364B (en) Preparation method of cross linking agent triallyl isocyanurate
CN103880625B (en) Method for preparing D, L-mandelic acid and derivative of D, L-mandelic acid
BRPI0922836B1 (en) process for the preparation of a monovalent succinate salt
CN111004162B (en) Method and device for preparing L-selenocysteine by using sodium triacetoxyborohydride as reducing agent
CN114988380A (en) Method for producing food-grade monopotassium phosphate and co-producing high-purity gypsum by using feed-grade calcium hydrophosphate
CN103332668A (en) Production method of monopotassium phosphate
CN113337548B (en) Preparation method of bio-based 1, 3-propylene glycol
CN108726569B (en) Preparation method of silver hexafluoroantimonate
CN108997154B (en) Betaine formulations with low sodium chloride content and low hygroscopicity
CN103804173A (en) Fermentation organic acid refining method
CN101747301B (en) Method for preparing vitamin C with low consumption
CN112678789A (en) Method for preparing monopotassium phosphate by using monoammonium phosphate clear liquid
CN104592004A (en) Long chain organic acid refining method
CN104591999A (en) Long chain organic acid purifying method
CN112159367A (en) Production method of high-quality 4-hydroxyethyl piperazine ethanesulfonic acid
CN117417394A (en) Method for recycling fructose from 5-hydroxymethylfurfural wastewater
CN115231990B (en) Preparation method of high-purity dipentaerythritol
CN102952165B (en) A kind of method extracting L-arabinose from xylose mother liquid
CN110606863B (en) Preparation method of N-acetylneuraminic acid dihydrate
CN106349108B (en) A kind of isolation and purification method of cyanoacetic acid
CN215403115U (en) Resource system for organic wastewater rich in sodium sulfate and ammonium sulfate
CN104355990A (en) Method for recycling and mechanically using L- (+) -tartaric acid in D-ethyl ester production
CN114605276A (en) Preparation method of glycine
CN109503325B (en) Method for reducing chroma of pentaerythritol
CN111233651A (en) Method for recovering and preparing L (+) -2, 3-dihydroxysuccinic acid from polybara production wastewater

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination