CN116328714A - Silicon-phosphorus modified alumina and application thereof to adsorption and regeneration of anionic dye - Google Patents

Silicon-phosphorus modified alumina and application thereof to adsorption and regeneration of anionic dye Download PDF

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CN116328714A
CN116328714A CN202310541924.1A CN202310541924A CN116328714A CN 116328714 A CN116328714 A CN 116328714A CN 202310541924 A CN202310541924 A CN 202310541924A CN 116328714 A CN116328714 A CN 116328714A
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silicon
phosphorus modified
adsorption
modified alumina
anionic dye
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宋家庆
李永建
陈帅奇
徐向宇
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Beijing University of Chemical Technology
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Beijing University of Chemical Technology
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    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/06Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising oxides or hydroxides of metals not provided for in group B01J20/04
    • B01J20/08Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising oxides or hydroxides of metals not provided for in group B01J20/04 comprising aluminium oxide or hydroxide; comprising bauxite
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/06Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising oxides or hydroxides of metals not provided for in group B01J20/04
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/28Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties
    • B01J20/28054Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties characterised by their surface properties or porosity
    • B01J20/28057Surface area, e.g. B.E.T specific surface area
    • B01J20/28061Surface area, e.g. B.E.T specific surface area being in the range 100-500 m2/g
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/28Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties
    • B01J20/28054Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties characterised by their surface properties or porosity
    • B01J20/28057Surface area, e.g. B.E.T specific surface area
    • B01J20/28064Surface area, e.g. B.E.T specific surface area being in the range 500-1000 m2/g
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/28Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties
    • B01J20/28054Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties characterised by their surface properties or porosity
    • B01J20/28069Pore volume, e.g. total pore volume, mesopore volume, micropore volume
    • B01J20/28076Pore volume, e.g. total pore volume, mesopore volume, micropore volume being more than 1.0 ml/g
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/30Processes for preparing, regenerating, or reactivating
    • B01J20/34Regenerating or reactivating
    • B01J20/3483Regenerating or reactivating by thermal treatment not covered by groups B01J20/3441 - B01J20/3475, e.g. by heating or cooling
    • 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
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/308Dyes; Colorants; Fluorescent agents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/34Organic compounds containing oxygen
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/38Organic compounds containing nitrogen
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/40Organic compounds containing sulfur
    • 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
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/30Wastewater or sewage treatment systems using renewable energies
    • Y02W10/37Wastewater or sewage treatment systems using renewable energies using solar energy

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Abstract

The invention discloses silicon-phosphorus modified alumina and application thereof to adsorption and regeneration of anionic dye. The method comprises the steps of dripping water glass and a compound containing phosphate radicals into a mixed solution of an aluminum sulfate solution and a sodium metaaluminate solution, and crystallizing to obtain slurry; filtering, washing and drying the slurry to obtain silicon-phosphorus modified boehmite; roasting the silicon-phosphorus modified boehmite at 600-1000 ℃ for 1-4h to obtain the silicon-phosphorus modified alumina. The prepared silicon-phosphorus modified alumina has large specific surface area and pore volume and has excellent adsorption effect on anionic dyes, especially Congo red and methyl blue. In addition, by utilizing the high thermal stability, the adsorption capacity of the high-temperature regeneration catalyst for 6 times is 96% of the primary adsorption capacity of Congo red and methyl blue. The adsorption and regeneration performances of the catalyst are superior to those of adsorption materials reported in literature, and the industrial wastewater treatment cost is further reduced.

Description

Silicon-phosphorus modified alumina and application thereof to adsorption and regeneration of anionic dye
Technical Field
The invention belongs to the technical field of modified alumina, and particularly relates to silicon-phosphorus modified alumina and application thereof to adsorption and regeneration of anionic dye.
Background
Organic waste materials in waste water of pharmaceutical industry and dye industry can severely pollute the environment, and the organic waste materials generally have the characteristics of high toxicity, easy carcinogenesis and difficult degradation, so the method has important significance for the treatment and research of the pollutants, such as environmental safety, people health and the like.
At present, in the treatment of organic matter-containing wastewater in the pharmaceutical industry, an important method is spray drying and then high-temperature incineration, but the problems of complex operation, high equipment requirement and high energy consumption exist; if the organic matter is adsorbed by the adsorbent in the waste water containing the organic matter, and then the adsorbent adsorbing the organic matter is roasted, the method is more economical, the operation is simple, the adsorbent can be recycled, and the key of industrial application of the method is that the adsorbent has excellent thermal stability in the high-temperature regeneration process. The active alumina has larger specific surface area and pore volume, the isoelectric point is generally more than 7, and more of the active alumina is used as an adsorption material of industrial anionic dye in recent years, but the specific surface area and pore volume of the active alumina can be greatly reduced due to self sintering and crystal form change under high-temperature roasting, which is unfavorable for repeated use. The thermal stability of the alumina can be improved by modifying the alumina, so that the alumina adsorbent has certain regeneration performance.
Disclosure of Invention
The invention aims to solve the problem that the adsorption quantity of an alumina adsorbent in the prior art is reduced more during re-adsorption after high-temperature regeneration, and provides a silicon-phosphorus modified alumina adsorbent with high thermal stability, which is applied to the adsorption of anionic dyes in water and repeated circularity after regeneration. The adsorbent has strong thermal stability and good regeneration performance, can still maintain extremely strong adsorption effect after multiple regenerations, and greatly reduces the treatment cost of industrial wastewater.
The preparation method of the silicon-phosphorus modified alumina comprises the following steps: dripping water glass and a phosphate radical-containing compound into a mixed solution of an aluminum sulfate solution and a sodium metaaluminate solution, and crystallizing to obtain slurry; filtering, washing and drying the slurry to obtain silicon-phosphorus modified boehmite; roasting the silicon-phosphorus modified boehmite at 600-1000 ℃ for 1-4h to obtain the silicon-phosphorus modified alumina.
The roasting temperature is 400-600 ℃, and the roasting time is 2-3h.
The phosphate radical-containing compound is one or more of disodium hydrogen phosphate, sodium dihydrogen phosphate, dipotassium hydrogen phosphate and potassium dihydrogen phosphate.
The concentration of the aluminum sulfate solution is 0.1-0.7mol/kg.
The molar ratio of the phosphate-containing compound to the sodium metaaluminate to the aluminum sulfate to the aluminum is 0.01-0.21:0.02-0.71:1, preferably 0.02-0.15:0.03-0.41:1, calculated by silicon element and calculated by phosphorus element.
The specific surface area of the silicon-phosphorus modified boehmite is 500-800m2/g,21-700m2/g, and the pore volume is 0.2-4cm3/g, preferably 3-4cm3/g.
The silicon-phosphorus modified alumina prepared by the method is used as an anionic dye adsorbent in water.
The use method of the silicon-phosphorus modified alumina as an anion dye adsorbent in water comprises the following steps: dispersing silicon-phosphorus modified alumina in an aqueous solution containing anionic dye, stirring for 1-20h, and filtering to remove the anionic dye in the water by adsorption; filtering after the adsorption is finished, drying, and roasting at 400-1000 ℃ for 1-4 hours to finish the desorption regeneration of the adsorbent.
The addition amount of the silicon phosphorus modified alumina in the aqueous solution containing the anionic dye is 0.1-2.0g/L.
The concentration of the anionic dye in the aqueous solution containing the anionic dye is 50-800mg/L, and the pH value of the solution is 2.0-13.0.
The silicon-phosphorus modified alumina prepared by using the cheap and easily available raw materials has large specific surface area and pore volume, and has excellent adsorption effect on anionic dyes, especially Congo red and methyl blue, wherein the adsorption capacity on Congo red can reach 1051.8mg/g, and the adsorption capacity on methyl blue can reach 1312.1mg/g. In addition, by utilizing the high thermal stability, the adsorption capacity of the high-temperature regeneration catalyst for 6 times is 96% of the primary adsorption capacity of Congo red and methyl blue. The adsorption and regeneration performances of the catalyst are superior to those of adsorption materials reported in literature, and the industrial wastewater treatment cost is further reduced.
Detailed Description
The endpoints and any values of the ranges disclosed herein are not limited to the precise range or value, and are understood to encompass values approaching those ranges or values. For numerical ranges, one or more new numerical ranges may be found between the endpoints of each range, between the endpoint of each range and the individual point value, and between the individual point value, in combination with each other, and are to be considered as specifically disclosed herein.
Example 1
(1) Adding water glass and disodium hydrogen phosphate into a mixed solution of an aluminum sulfate solution and a sodium metaaluminate solution in a dropwise manner (the Si/Al molar ratio is 0.074, the P/Al molar ratio is 0.087 and the concentration of the aluminum sulfate solution is 0.5 mol/kg), and crystallizing to obtain a slurry; filtering, washing and drying the slurry to obtain silicon-phosphorus modified boehmite; the silicon-phosphorus modified boehmite is roasted for 4 hours at the temperature of 600 ℃ to obtain silicon-phosphorus modified alumina with the specific surface area of 515.2m < 2 >/g and the pore volume of 1.48cm < 3 >/g.
(2) Dispersing 0.2g of silicon phosphorus modified alumina obtained in the step (1) in a Congo red solution with the concentration of 200mg/L and the pH of 7.7, stirring for 10 hours at room temperature, and filtering to finish the adsorption. The adsorption capacity is 906.8mg/L.
(3) The filtered silicon-phosphorus modified alumina is dried, and after roasting for 2 hours at 600 ℃, the regeneration is completed once, the specific surface area is 462.8m2/g, and the pore volume is 1.47cm3/g. The regenerated silicon-phosphorus modified alumina is filtered out after Congo red is adsorbed by the same condition as (2), and the adsorption capacity is 903.8mg/L.
(4) And (3) drying the filtered silicon-phosphorus modified alumina, and roasting at 600 ℃ for 2 hours to complete the second regeneration, wherein the specific surface area is 437.0m2/g, and the pore volume is 1.45cm3/g. The silicon phosphorus-modified alumina regenerated twice was filtered out after adsorbing Congo red using the same conditions as in (2) in example 1, and the adsorption capacity was 905.3mg/L.
(5) The filtered silicon-phosphorus modified alumina is dried, baked for 2 hours at 600 ℃ and then regenerated for the third time, wherein the specific surface area is 428.4m2/g, and the pore volume is 1.42cm3/g. The silicon phosphorus-modified alumina was collected and regenerated three times, and was filtered out after adsorbing Congo red using the same conditions as in (2) in example 1, and its adsorption capacity was 899.4mg/L.
Example 2
(1) 0.2g of the silicon phosphorus modified alumina prepared in the step (1) of example 1 was dispersed in a methyl blue solution having a concentration of 200mg/L and a pH of 5.2, stirred at room temperature for 8 hours, and then filtered to complete adsorption. The adsorption capacity is 822.7mg/L.
(2) The filtered silicon-phosphorus modified alumina was dried, and after 2 hours of calcination at 600 ℃, the regeneration was completed once, with a specific surface area of 467.8m2/g and a pore volume of 1.42cm3/g. The regenerated silicon-phosphorus modified alumina is filtered out after methyl blue is adsorbed by the same condition as (1), and the adsorption capacity is 822.7mg/L.
(3) The filtered silicon-phosphorus modified alumina is dried and baked for 2 hours at 600 ℃ to complete the second regeneration, the specific surface area is 460.6m2/g, and the pore volume is 1.42cm3/g. The silicon-phosphorus modified alumina regenerated twice is taken, methyl blue is adsorbed by the same condition as in (1) and filtered out, and the adsorption capacity is 822.1mg/L.
(4) The filtered silicon-phosphorus modified alumina was dried, and after roasting at 600℃for 2 hours, the third regeneration was completed, with a specific surface area of 446.7m2/g and a pore volume of 1.41cm3/g. The silicon phosphorus modified alumina which is regenerated three times is taken, methyl blue is adsorbed by the same condition as the (1) and filtered out, and the adsorption capacity is 815.6mg/L.
Comparative example 1
The adsorption was performed according to the same conditions as in example 1, except that: alumina (specific surface area 180.4m2/g, pore volume 1.53cm 3/g) calcined from commercial SB powder was used as the adsorbent.
The adsorption capacity of the silicon carbide red is 341.7mg/L, the adsorption capacity of the silicon carbide red after regeneration is 284.0mg/L, and the adsorption capacity of the silicon carbide red after three times of regeneration is 121.3mg/L.
Comparative example 2
Adsorption was performed according to the same conditions as in example 2, except that: alumina calcined from commercial SB powder was used as the adsorbent.
The adsorption capacity of the catalyst for the methyl blue is 730.5mg/L, the adsorption capacity of the catalyst for the methyl blue after one regeneration is 546.1mg/L, and the adsorption capacity of the catalyst for the methyl blue after three regenerations is 468.1mg/L.
The preferred embodiments of the present invention have been described in detail above, but the present invention is not limited thereto. Within the scope of the technical idea of the invention, a number of simple variants of the technical solution of the invention are possible, including combinations of the individual technical features in any other suitable way, which simple variants and combinations should likewise be regarded as being disclosed by the invention, all falling within the scope of protection of the invention.

Claims (10)

1. The preparation method of the silicon-phosphorus modified alumina is characterized by comprising the following specific operations: dripping water glass and a phosphate radical-containing compound into a mixed solution of an aluminum sulfate solution and a sodium metaaluminate solution, and crystallizing to obtain slurry; filtering, washing and drying the slurry to obtain silicon-phosphorus modified boehmite; roasting the silicon-phosphorus modified boehmite at 600-1000 ℃ for 1-4h to obtain the silicon-phosphorus modified alumina.
2. The method according to claim 1, wherein the firing temperature is 400 to 600 ℃ and the firing time is 2 to 3 hours.
3. The method according to claim 1, wherein the phosphate group-containing compound is one or more of disodium hydrogen phosphate, sodium dihydrogen phosphate, dipotassium hydrogen phosphate and potassium dihydrogen phosphate.
4. The method according to claim 1, wherein the concentration of the aluminum sulfate solution is 0.1 to 0.7mol/kg.
5. The preparation method according to claim 1, wherein the molar ratio of phosphate-containing compound to sodium metaaluminate and aluminum sulfate to aluminum element is 0.01-0.21:0.02-0.71:1, preferably 0.02-0.15:0.03-0.41:1, calculated as silicon element and phosphorus element.
6. The preparation method according to claim 1, wherein the specific surface area of the silicon phosphorus modified boehmite is 500-800m2/g,21-700m2/g, and the pore volume is 0.2-4cm3/g, preferably 3-4cm3/g.
7. Use of the silicon phosphorus modified alumina prepared according to the method of any one of claims 1-6 as an anionic dye adsorbent in water.
8. The use of claim 7, wherein the silicon phosphorus modified alumina is used as an anionic dye adsorbent in water by: dispersing silicon-phosphorus modified alumina in an aqueous solution containing anionic dye, stirring for 1-20h, and filtering to remove the anionic dye in the water by adsorption; filtering after the adsorption is finished, drying, and roasting at 400-1000 ℃ for 1-4 hours to finish the desorption regeneration of the adsorbent.
9. The use according to claim 8, wherein the silicon phosphorus modified alumina is added to the aqueous solution containing the anionic dye in an amount of 0.1 to 2.0g/L.
10. The use according to claim 8, wherein the concentration of the anionic dye in the aqueous solution containing the anionic dye is 50-800mg/L and the pH of the solution is 2.0-13.0.
CN202310541924.1A 2023-05-15 2023-05-15 Silicon-phosphorus modified alumina and application thereof to adsorption and regeneration of anionic dye Pending CN116328714A (en)

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