CN114133058B - Friedel-crafts reaction aluminum-containing wastewater recycling method - Google Patents

Friedel-crafts reaction aluminum-containing wastewater recycling method Download PDF

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CN114133058B
CN114133058B CN202111273721.6A CN202111273721A CN114133058B CN 114133058 B CN114133058 B CN 114133058B CN 202111273721 A CN202111273721 A CN 202111273721A CN 114133058 B CN114133058 B CN 114133058B
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wastewater
aluminum
containing wastewater
friedel
crafts reaction
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CN114133058A (en
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刘晓蕾
曹倩倩
王雪
李晓艳
郭健琦
成道泉
刘志远
韦玉汉
房立彬
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Shandong Jingbo Agrochemical Technology Co ltd
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F9/00Multistage treatment of water, waste water or sewage
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01FCOMPOUNDS OF THE METALS BERYLLIUM, MAGNESIUM, ALUMINIUM, CALCIUM, STRONTIUM, BARIUM, RADIUM, THORIUM, OR OF THE RARE-EARTH METALS
    • C01F7/00Compounds of aluminium
    • C01F7/48Halides, with or without other cations besides aluminium
    • C01F7/56Chlorides
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/001Processes for the treatment of water whereby the filtration technique is of importance
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/281Treatment of water, waste water, or sewage by sorption using inorganic sorbents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/283Treatment of water, waste water, or sewage by sorption using coal, charred products, or inorganic mixtures containing them
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/722Oxidation by peroxides

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  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Geology (AREA)
  • Inorganic Chemistry (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)
  • Water Treatment By Sorption (AREA)

Abstract

The invention relates to the technical field of aluminum-containing wastewater treatment, in particular to a Friedel-crafts reaction aluminum-containing wastewater recycling method. Firstly, oxidizing and removing organic macromolecules in aluminum-containing wastewater by using an oxidant, then adsorbing particle impurities in the wastewater by using an adsorbent, refining the wastewater, dividing the refined wastewater into two parts, adding alkali into one part of the wastewater to prepare sodium metaaluminate, dripping the prepared sodium metaaluminate into the other part of the wastewater, and polymerizing and curing to prepare the polyaluminium chloride. The method prepares the polyaluminium chloride while treating the aluminum-containing wastewater, has low three-waste generation amount, and greatly reduces the subsequent treatment cost and the influence on the environment. The basicity of the polyaluminum chloride prepared by the method is 88% -95%, and the content of the aluminum oxide can reach 28% -30%.

Description

Friedel-crafts reaction aluminum-containing wastewater recycling method
Technical Field
The invention relates to the technical field of aluminum-containing wastewater treatment, in particular to a Friedel-crafts reaction aluminum-containing wastewater recycling method.
Background
In the production process of pesticides and intermediates thereof, alkyl hydrocarbon and aromatic ketone compounds are often synthesized by utilizing Friedel-crafts reaction, aluminum trichloride is commonly used as a catalyst in Friedel-crafts reaction, and waste water generated by the process contains the aluminum trichloride catalyst, so that the content of aluminum ions in the waste water is high, and the waste water is directly discharged to an oxidation pond for biodegradation, so that flora poisoning can be caused, and the aim of treatment cannot be achieved. Meanwhile, aluminum ions have high toxicity to human bodies, and the aluminum ions in industrial wastewater can be discharged only after being treated by less than 5 ppm. The common treatment technology is to treat aluminum ions in the wastewater to the emission standard by adopting a complexing method through a precipitation method, such as the treatment method of aluminum-containing wastewater generated by a Friedel-crafts reaction (CN201810019313. X), but the technology can generate a large amount of aluminum mud solid waste, so that serious secondary pollution is caused, the treatment cost is high, and meanwhile, the aluminum mud is discarded as the solid waste to cause waste. While CN202110180294.0 discloses a method for treating aluminum trichloride wastewater, which is used for preparing polyaluminium chloride by treating wastewater, however, the patent needs to be treated by extraction, rectification and the like during wastewater treatment, and has long flow, high cost, and is easy to introduce ketone organic solvents during treatment, difficult to remove, brings impurities and affects the purity of products.
Disclosure of Invention
Aiming at the technical problems that solid waste is generated and aluminum resources are wasted in aluminum-containing wastewater treatment in the prior art, the invention aims to provide a method for recycling aluminum-containing wastewater in Friedel-crafts reaction, which can treat the aluminum-containing wastewater in Friedel-crafts reaction and can simultaneously utilize the recovered aluminum to prepare polyaluminium chloride.
The invention provides a Friedel-crafts reaction aluminum-containing wastewater recycling method, which comprises the following steps:
(1) Adding an oxidant into the aluminum-containing wastewater, oxidizing, adding an adsorbent, and filtering to obtain wastewater A;
(2) Dividing wastewater A into wastewater A 1 And waste water A 2
(3) Preparing alkali liquor, and dropwise adding wastewater A into the alkali liquor 1 Preparing a mixed solution B containing sodium metaaluminate;
(4) Waste water A 2 Heating, starting stirring, dropwise adding the mixed solution B, preserving heat after the dropwise adding is finished, cooling after the heat preservation, standing and curing to obtain supernatant polyaluminium chloride liquid;
(6) Concentrating and drying supernatant polyaluminium chloride liquid to obtain a solid polyaluminium chloride finished product.
Further, the total mass of the wastewater A is m, and the wastewater A 1 Mass is m 1 Waste water A 2 Is of mass m 2 ,m 1 =15%m,m 2 =85%m. Based on stable production in workshops, the same batch of wastewater has the mass of 15: 85% of the waste water is separated, 15% of the waste water is used for preparing sodium metaaluminate, the rest 85% of the waste water reacts with the prepared sodium metaaluminate to prepare polyaluminum chloride, the polyaluminum chloride obtained according to the proportion reaches the qualification standard, and a batch of waste water is just consumed, so that the waste water utilization rate is greatly improved.
Further, the oxidant is hydrogen peroxide, the consumption of the oxidant is 0.5-5% of the total mass of the aluminum-containing wastewater, and the oxidation time of the oxidant is 0.5-3h.
Further, the adsorbent is one of activated carbon, diatomite and activated alumina.
Further, the amount of the adsorbent is 0.5-2% of the total mass of the aluminum-containing wastewater, the wastewater is heated to 30-60 ℃ after being added with the adsorbent, and the wastewater is stirred and kept for 0.5-3 hours.
Further, the alkali liquor is sodium hydroxide solution, the mass concentration of the alkali liquor is 35-50%, and the dripping time is 4 hours.
Further, waste water A 2 Heating to 100-150deg.C, and stirring at 1500-3000r/min.
Further, the dripping time of the mixed solution B is 6-10h, the temperature is kept for 1-4h after the dripping is finished, and the temperature is reduced to 25-30 ℃ after the temperature is kept.
Further, standing and curing for 48-96h, mixing the lower layer solid insoluble substance with the mixed solution B after standing and curing, and continuing curing and polymerization to prepare sodium metaaluminate.
Further, in the step (5), concentrated and dried effluent is introduced into the alkali liquor in the step (3) for recycling.
The principle of the invention is as follows: firstly, oxidizing and removing organic macromolecules in aluminum-containing wastewater by using an oxidant, then, adsorbing granular impurities in the wastewater by using an adsorbent, refining the wastewater, dividing the refined wastewater into two parts, adding alkali into one part of the wastewater to prepare sodium metaaluminate, dripping the prepared sodium metaaluminate into the other part of the wastewater to react to generate aluminum hydroxide precipitate, and generating polyaluminium chloride under the conditions of high temperature and rapid stirring and the action of hydrochloric acid existing in a system, wherein the specific reaction equation is as follows:
the invention has the beneficial effects that (1) the aluminum-containing wastewater is divided into two parts, other polymerization raw materials are not needed, aluminum chloride is prepared while the aluminum-containing wastewater is treated, the three wastes are generated, the utilization rate of the wastewater is improved, and the subsequent treatment cost and the influence on the environment are greatly reduced. (2) The invention changes the aluminum element in the wastewater into valuable, and does not produce secondary pollution in the preparation process of the polyaluminium chloride. (3) The polyaluminium chloride prepared by the method has the basicity of 88% -95%, the content of alumina can reach 28% -30%, and the polyaluminium chloride has a good flocculation precipitation effect and can be used as a water purifying agent.
Drawings
In order to more clearly illustrate the embodiments of the present invention or the technical solutions in the prior art, the drawings that are required to be used in the description of the embodiments or the prior art will be briefly described below, and it will be obvious to those skilled in the art that other drawings can be obtained from these drawings without inventive effort.
FIG. 1 is a process flow diagram of an embodiment of the present invention.
Detailed Description
In order to make the technical solution of the present invention better understood by those skilled in the art, the technical solution of the present invention will be clearly and completely described below with reference to the accompanying drawings in the embodiments of the present invention, and it is apparent that the described embodiments are only some embodiments of the present invention, not all embodiments. All other embodiments, which can be made by those skilled in the art based on the embodiments of the present invention without making any inventive effort, shall fall within the scope of the present invention.
Examples 1-5 are aluminum-containing wastewater after Friedel-crafts reaction, and FIG. 1 shows a process flow of an embodiment of the invention.
Example 1
The invention relates to a Friedel-crafts reaction aluminum-containing wastewater recycling method, which comprises the following steps:
(1) Wastewater refining: adding 900kg of hydrogen peroxide into 30 tons of aluminum-containing wastewater, uniformly mixing, standing for oxidation for 2 hours, adding 600kg of fresh activated carbon after the oxidation is finished, heating to 60 ℃, stirring, preserving heat for 2 hours, and filtering to obtain 29.5 tons of refined wastewater;
(2) Preparation of sodium metaaluminate: mixing 4.43 tons of refined wastewater in the step (1) with industrial water and analytically pure sodium hydroxide solid, preparing alkali liquor with the mass concentration of 4.43 tons and 35 percent, and dripping the 4.43 tons of refined wastewater into the alkali liquor for 4 hours to obtain high-concentration sodium metaaluminate;
(3) And (3) polymerization curing: heating the remaining 25.07 tons of refined wastewater in the step (1) to 105 ℃, stirring at a rotating speed of 1500r/min, slowly and uniformly dropwise adding sodium metaaluminate in the step (2) for 8 hours, preserving heat for 2 hours after the dropwise adding is finished, cooling to 25-30 ℃ after the heat preservation is finished, standing and curing for 72 hours, and obtaining supernatant which is liquid polyaluminium chloride;
(4) And (3) drying and packaging: concentrating and drying the liquid polyaluminium chloride obtained after standing and curing in the step (3) to obtain finished solid polyaluminium chloride, introducing the concentrated and dried alkaline effluent into the alkali liquor in the step (2) for recycling, wherein the collection of the concentrated and dried effluent is realized by condensation;
(5) And (3) recycling: mixing the solid insoluble substance at the bottom left after standing and curing in the step (3) with the high-concentration sodium metaaluminate in the step (2), and continuing curing and polymerization to prepare the sodium metaaluminate.
By examining the polyaluminium chloride produced in this example, as shown in Table 1, the solid polyaluminium chloride index after the aluminum-containing wastewater produced in the Friedel-crafts reaction of example 1 is shown.
Table 1 example 1 preparation of polyaluminum chloride detection index
Project Alumina content Basicity degree
Content of 29.3% 88%
Example 2
(1) Wastewater refining: adding 900kg of hydrogen peroxide into 30 tons of aluminum-containing wastewater, uniformly mixing, standing for oxidation for 2 hours, adding 300kg of fresh activated carbon after the oxidation is finished, heating to 60 ℃, stirring, preserving heat for 2 hours, and filtering to obtain 29.5 tons of refined wastewater;
(2) Preparation of sodium metaaluminate: mixing 4.43 tons of refined wastewater in the step (1) with industrial water and analytically pure sodium hydroxide solid, preparing alkali liquor with the mass concentration of 4.43 tons and 35 percent, and dripping the 4.43 tons of refined wastewater into the alkali liquor for 4 hours to obtain high-concentration sodium metaaluminate;
(3) And (3) polymerization curing: heating the remaining 25.07 tons of refined wastewater in the step (1) to 105 ℃, stirring at a rotation speed of 2000r/min, slowly and uniformly dropwise adding sodium metaaluminate in the step (2) for 8 hours, preserving heat for 2 hours after the dropwise adding is finished, cooling to 25-30 ℃ after the heat preservation is finished, standing and curing for 96 hours, and obtaining supernatant which is liquid polyaluminium chloride;
(4) And (3) drying and packaging: concentrating and drying the liquid polyaluminium chloride obtained after standing and curing in the step (3) to obtain finished solid polyaluminium chloride, introducing the concentrated and dried alkaline effluent into the alkali liquor in the step (2) for recycling, wherein the collection of the concentrated and dried effluent is realized by condensation;
(5) And (3) recycling: mixing the solid insoluble substance at the bottom left after standing and curing in the step (3) with the high-concentration sodium metaaluminate in the step (2), and continuing curing and polymerization to prepare the sodium metaaluminate.
By examining the polyaluminium chloride produced in this example, as shown in Table 2, the solid polyaluminium chloride index after the aluminum-containing wastewater produced in the Friedel-crafts reaction of example 2 is shown.
Table 2 example 2 preparation of polyaluminum chloride detection index
Project Alumina content Basicity degree
Content of 29.8% 91%
Example 3
(1) Wastewater refining: adding 150kg of hydrogen peroxide into 30 tons of aluminum-containing wastewater, uniformly mixing, standing for oxidation for 0.5 hour, adding 150kg of fresh diatomite after oxidation, heating to 30 ℃, stirring, preserving heat for 0.5 hour, and filtering to obtain 29.8 tons of refined wastewater;
(2) Preparation of sodium metaaluminate: mixing 4.43 tons of refined wastewater in the step (1) with industrial water and analytically pure sodium hydroxide solid, preparing alkali liquor with the mass concentration of 4.43 tons and 50%, and dripping the 4.43 tons of refined wastewater into the alkali liquor for 4 hours to obtain high-concentration sodium metaaluminate;
(3) And (3) polymerization curing: heating the rest 25.33 tons of refined wastewater in the step (1) to 150 ℃, slowly and uniformly dropwise adding sodium metaaluminate in the step (2) at a stirring rotating speed of 3000r/min for 6 hours, preserving heat for 1 hour after the dropwise adding is finished, cooling to 25-30 ℃ after the heat preservation is finished, standing and curing for 48 hours, and obtaining supernatant which is liquid polyaluminium chloride;
(4) And (3) drying and packaging: concentrating and drying the liquid polyaluminium chloride obtained after standing and curing in the step (3) to obtain finished solid polyaluminium chloride, introducing the concentrated and dried alkaline effluent into the alkali liquor in the step (2) for recycling, wherein the collection of the concentrated and dried effluent is realized by condensation;
(5) And (3) recycling: mixing the solid insoluble substance at the bottom left after standing and curing in the step (3) with the high-concentration sodium metaaluminate in the step (2), and continuing curing and polymerization to prepare the sodium metaaluminate.
By examining the polyaluminium chloride produced in this example, as shown in Table 3, the solid polyaluminium chloride index after the aluminum-containing wastewater produced in the Friedel-crafts reaction of example 3 is shown.
TABLE 3 example 3 preparation of polyaluminum chloride detection index
Project Alumina content Basicity degree
Content of 30.2% 95%
Example 4
(1) Wastewater refining: adding 600kg of hydrogen peroxide into 30 tons of aluminum-containing wastewater, uniformly mixing, standing for oxidation for 3 hours, adding 600kg of fresh diatomite after oxidation, heating to 40 ℃, stirring, preserving heat for 3 hours, and filtering to obtain 29 tons of refined wastewater;
(2) Preparation of sodium metaaluminate: mixing 4.35 tons of refined wastewater in the step (1) with industrial water and analytically pure sodium hydroxide solid, preparing alkali liquor with the mass concentration of 4.43 tons and 50%, and dripping the 4.43 tons of refined wastewater into the alkali liquor for 4 hours to obtain high-concentration sodium metaaluminate;
(3) And (3) polymerization curing: heating the rest 15.65 tons of refined wastewater in the step (1) to 100 ℃, slowly and uniformly dropwise adding sodium metaaluminate in the step (2) at a stirring rotating speed of 2000r/min for 10 hours, preserving heat for 4 hours after the dropwise adding is finished, cooling to 25-30 ℃ after the heat preservation is finished, standing and curing for 50 hours, and obtaining supernatant which is liquid polyaluminium chloride;
(4) And (3) drying and packaging: concentrating and drying the liquid polyaluminium chloride obtained after standing and curing in the step (3) to obtain finished solid polyaluminium chloride, introducing the concentrated and dried alkaline effluent into the alkali liquor in the step (2) for recycling, wherein the collection of the concentrated and dried effluent is realized by condensation;
(5) And (3) recycling: mixing the solid insoluble substance at the bottom left after standing and curing in the step (3) with the high-concentration sodium metaaluminate in the step (2), and continuing curing and polymerization to prepare the sodium metaaluminate.
By examining the polyaluminium chloride produced in this example, as shown in Table 4, the solid polyaluminium chloride index after the aluminum-containing wastewater produced in the Friedel-crafts reaction of example 4 is shown.
TABLE 4 example 4 preparation of polyaluminum chloride detection index
Project Alumina content Basicity degree
Content of 28.3% 93%
Example 5
(1) Wastewater refining: adding 1500kg of hydrogen peroxide into 30 tons of aluminum-containing wastewater, uniformly mixing, standing for oxidization for 1 hour, adding 600kg of fresh diatomite after oxidization, heating to 50 ℃, stirring, preserving heat for 3 hours, and filtering to obtain 28.6 tons of purified wastewater;
(2) Preparation of sodium metaaluminate: mixing 4.29 tons of refined wastewater in the step (1) with industrial water and analytically pure sodium hydroxide solid, preparing alkali liquor with the mass concentration of 4.29 tons and 50%, and dripping the 4.29 tons of refined wastewater into the alkali liquor for 4 hours to obtain high-concentration sodium metaaluminate;
(3) And (3) polymerization curing: heating the rest 24.31 tons of refined wastewater in the step (1) to 100 ℃, slowly and uniformly dropwise adding sodium metaaluminate in the step (2) at a stirring rotating speed of 2000r/min for 10 hours, preserving heat for 4 hours after the dropwise adding is finished, cooling to 25-30 ℃ after the heat preservation is finished, standing and curing for 60 hours, and obtaining supernatant which is liquid polyaluminium chloride;
(4) And (3) drying and packaging: concentrating and drying the liquid polyaluminium chloride obtained after standing and curing in the step (3) to obtain finished solid polyaluminium chloride, introducing the concentrated and dried alkaline effluent into the alkali liquor in the step (2) for recycling, wherein the collection of the concentrated and dried effluent is realized by condensation;
(5) And (3) recycling: mixing the solid insoluble substance at the bottom left after standing and curing in the step (3) with the high-concentration sodium metaaluminate in the step (2), and continuing curing and polymerization to prepare the sodium metaaluminate.
By examining the polyaluminium chloride produced in this example, as shown in Table 5, the solid polyaluminium chloride index after the aluminum-containing wastewater produced in the Friedel-crafts reaction of example 5 is shown.
TABLE 5 example 5 preparation of polyaluminum chloride detection index
Project Alumina content Basicity degree
Content of 29.3% 94%
Comparative example 1
Comparative example 1 the process was as described in example 1, except that in comparative example 1, 2.95 tons of post-purification waste water was taken in step (2), and 26.55 tons of purified waste water was taken in step (3).
Comparative example 2
Comparative example 2 the procedure was as described in example 2, except that in comparative example 2, 5.9 tons of post-purification waste water was taken in step (2), and 23.6 tons of purified waste water was taken in step (3).
By examining the polyaluminium chloride prepared in comparative examples 1 and 2, the solid polyaluminium chloride index after the aluminum-containing wastewater preparation in comparative examples 1 and 2 is shown in Table 6.
Table 6 comparative examples 1 and 2 preparation of polyaluminum chloride detection index
Project Alumina content Basicity degree
Comparative example 1 25.9% 75%
Comparative example 2 23.3% 83%
As can be seen from the data in Table 6, the wastewater A was adjusted by comparative example 1 and comparative example 1, example 2 and comparative example 2 1 And waste water A 2 The proportion of the poly aluminum chloride is seriously influenced; waste water A 1 And waste water A 2 The influence of the proportion of the water-soluble polymer on the basicity of the polyaluminum chloride is obvious, and the utilization rate of the wastewater can be improved by reasonable proportion.
Although the present invention has been described in detail by way of preferred embodiments with reference to the accompanying drawings, the present invention is not limited thereto. Various equivalent modifications and substitutions may be made in the embodiments of the present invention by those skilled in the art without departing from the spirit and scope of the present invention, and it is intended that all such modifications and substitutions be within the scope of the present invention/be within the scope of the present invention as defined by the appended claims.

Claims (9)

1. A Friedel-crafts reaction aluminum-containing wastewater recycling method is characterized by comprising the following steps:
(1) Adding an oxidant into the aluminum-containing wastewater, oxidizing, adding an adsorbent, and filtering to obtain wastewater A;
(2) Dividing wastewater A into wastewater A 1 And waste water A 2 The total mass of the wastewater A is m, and the wastewater A 1 Mass is m 1 Waste water A 2 Is of mass m 2 ,m 1 =15%m,m 2 =85%m;
(3) Preparing alkali liquor, and dropwise adding wastewater A into the alkali liquor 1 Preparing a mixed solution B containing sodium metaaluminate;
(4) Waste water A 2 Heating, starting stirring, dropwise adding the mixed solution B, preserving heat after the dropwise adding is finished, cooling after the heat preservation, standing and curing to obtain supernatant polyaluminium chloride liquid;
(5) Concentrating and drying supernatant polyaluminium chloride liquid to obtain a solid polyaluminium chloride finished product.
2. The method for recycling aluminum-containing wastewater of Friedel-crafts reaction according to claim 1, wherein the oxidant is hydrogen peroxide, the consumption of the oxidant is 0.5-5% of the total mass of the aluminum-containing wastewater, and the oxidation time of the oxidant is 0.5-3h.
3. The method for recycling aluminum-containing wastewater of friedel-crafts reaction according to claim 1, wherein the adsorbent is one of activated carbon, diatomaceous earth and activated alumina.
4. The method for recycling aluminum-containing wastewater by friedel-crafts reaction according to claim 3, wherein the amount of the adsorbent is 0.5-2% of the total mass of the aluminum-containing wastewater, the wastewater is heated to 30-60 ℃ after being added with the adsorbent, and the stirring and the heat preservation are carried out for 0.5-3 hours.
5. The method for recycling aluminum-containing wastewater of Friedel-crafts reaction according to claim 1, wherein the alkaline solution is sodium hydroxide solution, the mass concentration of the alkaline solution is 35-50%, and the dripping time is 4h.
6. The method for recycling aluminum-containing wastewater of Friedel-crafts reaction according to claim 1, wherein the wastewater A 2 Heating to 100-150deg.C, and stirring at 1500-3000r/min.
7. The method for recycling aluminum-containing wastewater of Friedel-crafts reaction according to claim 1, wherein the dropwise adding time of the mixed solution B is 6-10h, the temperature is kept for 1-4h after the dropwise adding is completed, and the temperature is reduced to 25-30 ℃ after the temperature is kept.
8. The method for recycling aluminum-containing wastewater of Friedel-crafts reaction according to claim 1, wherein the standing and curing time is 48-96h, and the lower layer solid insoluble substance is mixed with the mixed solution B after standing and curing, and the curing and polymerization are continued to prepare sodium metaaluminate.
9. The method for recycling aluminum-containing wastewater in Friedel-crafts reaction according to claim 1, wherein the concentrated and dried effluent in the step (5) is recycled in the alkali liquor in the step (3).
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Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP1690834A2 (en) * 2005-02-14 2006-08-16 Sachtleben Chemie GmbH Polyaluminum chloride solution
CN101633594A (en) * 2009-08-20 2010-01-27 镇江市海通化工有限公司 Environmental-friendly Friedel-Crafts reaction postprocessing method
CN105417563A (en) * 2015-12-10 2016-03-23 建德市环保科技创新创业中心有限公司 Method for preparing poly-aluminum chloride from waste aluminum salt liquid discharged in production process of essence and flavor
CN106673040A (en) * 2016-12-19 2017-05-17 天津利安隆新材料股份有限公司 Method for recycling polyaluminum chloride by utilizing alchlor wastewater for compounding triazines ultraviolet absorber
CN107324363A (en) * 2017-07-28 2017-11-07 中国科学院生态环境研究中心 A kind of high Al13The simple method for preparing of content aluminium polychloride
CN108249697A (en) * 2018-01-09 2018-07-06 上海化学试剂研究所有限公司 A kind of processing method for the aluminium wastewater that Friedel-Crafts reaction generates
CN111252791A (en) * 2020-01-18 2020-06-09 斯瑞尔环境科技股份有限公司 Comprehensive utilization method of high-aluminum-content waste alkali liquor
CN111875486A (en) * 2020-07-13 2020-11-03 京博农化科技有限公司 Synthesis method of 2, 6-dimethyl-1-indanone
CN113247996A (en) * 2021-02-08 2021-08-13 江苏扬农化工股份有限公司 Method for treating aluminum trichloride wastewater

Patent Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP1690834A2 (en) * 2005-02-14 2006-08-16 Sachtleben Chemie GmbH Polyaluminum chloride solution
CN101633594A (en) * 2009-08-20 2010-01-27 镇江市海通化工有限公司 Environmental-friendly Friedel-Crafts reaction postprocessing method
CN105417563A (en) * 2015-12-10 2016-03-23 建德市环保科技创新创业中心有限公司 Method for preparing poly-aluminum chloride from waste aluminum salt liquid discharged in production process of essence and flavor
CN106673040A (en) * 2016-12-19 2017-05-17 天津利安隆新材料股份有限公司 Method for recycling polyaluminum chloride by utilizing alchlor wastewater for compounding triazines ultraviolet absorber
CN107324363A (en) * 2017-07-28 2017-11-07 中国科学院生态环境研究中心 A kind of high Al13The simple method for preparing of content aluminium polychloride
CN108249697A (en) * 2018-01-09 2018-07-06 上海化学试剂研究所有限公司 A kind of processing method for the aluminium wastewater that Friedel-Crafts reaction generates
CN111252791A (en) * 2020-01-18 2020-06-09 斯瑞尔环境科技股份有限公司 Comprehensive utilization method of high-aluminum-content waste alkali liquor
CN111875486A (en) * 2020-07-13 2020-11-03 京博农化科技有限公司 Synthesis method of 2, 6-dimethyl-1-indanone
CN113247996A (en) * 2021-02-08 2021-08-13 江苏扬农化工股份有限公司 Method for treating aluminum trichloride wastewater

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