CN116854260B - Sustained-release sewage treatment agent and preparation method thereof - Google Patents

Sustained-release sewage treatment agent and preparation method thereof Download PDF

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CN116854260B
CN116854260B CN202310937868.3A CN202310937868A CN116854260B CN 116854260 B CN116854260 B CN 116854260B CN 202310937868 A CN202310937868 A CN 202310937868A CN 116854260 B CN116854260 B CN 116854260B
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slow
release
parts
surfactant
sewage treatment
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CN116854260A (en
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柴建中
柴伟贺
左浩
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Hangzhou Jieshen Environmental Technology Co ltd
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Hangzhou Jieshen Environmental 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
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/34Biological treatment of water, waste water, or sewage characterised by the microorganisms used
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J13/00Colloid chemistry, e.g. the production of colloidal materials or their solutions, not otherwise provided for; Making microcapsules or microballoons
    • B01J13/02Making microcapsules or microballoons
    • B01J13/06Making microcapsules or microballoons by phase separation
    • B01J13/14Polymerisation; cross-linking
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/16Nitrogen compounds, e.g. ammonia
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/20Heavy metals or heavy metal compounds
    • 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
    • Y02W10/10Biological treatment of water, waste water, or sewage

Abstract

The invention relates to the technical field of sewage treatment, in particular to a slow-release sewage treatment agent and a preparation method thereof, wherein the sewage treatment agent comprises the following raw materials in parts by weight: 40-50 parts of slow release microspheres, 4-6 parts of thickening agent, 8-10 parts of surfactant, 20-30 parts of flocculating agent, 5-10 parts of metal oxide and 3-5 parts of dispersing agent. The sewage treatment agent not only can cooperatively treat high ammonia nitrogen, COD, heavy metal ions and some micromolecular harmful substances in sewage, has excellent sewage purification effect, but also has a good slow release function, and achieves the effect of long-acting utilization.

Description

Sustained-release sewage treatment agent and preparation method thereof
Technical Field
The invention relates to the technical field of sewage treatment, in particular to a slow-release sewage treatment agent and a preparation method thereof.
Background
Along with the vigorous development of economy, the productivity is continuously accelerated, the sewage discharge amount is also rapidly increased, and the sewage can cause secondary pollution to the environment if being improperly treated, thereby further threatening the ecological environment and human health. Ammonia nitrogen and COD in sewage can cause water quality deterioration, so that water body unbalance is caused, the survival of animals and plants in the water body is influenced, meanwhile, heavy metal ions and compounds thereof in the sewage can be enriched in fish and other aquatic organisms, and serious harm is caused to human beings and surrounding ecological environment through the circulation of drinking water and food chains.
At present, the method for sewage treatment mainly comprises a chemical method and a biological method, wherein the chemical method is to add medicines into a water body to achieve the effect of water purification, but due to complex pollutant types of sewage, the existing water treatment agents are difficult to cooperatively treat various pollutants such as ammonia nitrogen, COD and heavy metal ions, and the effect of sewage purification is poor; for biological methods, a certain microbial agent is added into a water body for multiple times to realize the purification effect, but microorganisms directly added into the water body exist in a free mode, so that the microorganisms are seriously lost and cannot be applied in the water body for a long time, and the purification effect on sewage is limited.
Disclosure of Invention
In order to overcome the defects in the prior art, the invention provides a slow-release sewage treatment agent and a preparation method thereof, and the sewage treatment agent not only can remove ammonia nitrogen in sewage, reduce COD content and purify heavy metals, but also has a good slow-release function, can slowly release strains in a water body, and achieves the effect of long-acting utilization.
In order to achieve the above purpose, the technical scheme adopted by the invention is as follows:
The invention provides a slow-release sewage treatment agent, which comprises the following raw materials in parts by weight: 40-50 parts of slow release microspheres, 4-6 parts of thickening agent, 8-10 parts of surfactant, 20-30 parts of flocculating agent, 5-10 parts of metal oxide and 3-5 parts of dispersing agent.
In some embodiments, the preparation of the sustained release microsphere comprises the steps of:
(1) Dissolving diamine monomer and grafting monomer in N, N-dimethylformamide to obtain phase A, dispersing nonionic surfactant in liquid paraffin to obtain phase B, mixing the phase A and the phase B under stirring to form a nonaqueous emulsion system, adding dianhydride monomer to react for 4-6 hours to obtain polymer, adding a mixture of acetic anhydride and pyridine to perform chemical imidization to obtain precipitate, washing and drying the precipitate, performing thermal imidization to obtain modified polyimide polymer, and performing heat treatment on the modified polyimide polymer at 190 ℃ for 1 hour to obtain a modified polyimide porous carrier;
(2) Adding the modified polyimide porous carrier prepared in the step (1) into a strain solution, soaking for 2-3h, taking out, and drying to obtain microspheres loaded with strains;
(3) And (3) adding the strain-loaded microspheres obtained in the step (2) into a slow-release film solution, uniformly mixing, and drying to obtain the slow-release microspheres.
The molar ratio of the diamine monomer to the dianhydride monomer is 1:1.07, wherein the diamine monomer is 4,4' -diaminodiphenyl ether, the dianhydride monomer is pyromellitic dianhydride, the addition amount of the grafting monomer is 30wt% of the dianhydride monomer, the nonionic surfactant comprises span 85 and tween 80, and the weight ratio of the span 85 to the tween 80 is 1.8: the addition amount of the mixture of the acetic anhydride and the pyridine is 12% of the volume of the N, N-dimethylformamide, and the volume ratio of the acetic anhydride to the pyridine in the mixture of the acetic anhydride and the pyridine is 2:1.
The grafting monomer is obtained by the following steps: polyethylene glycol, 3, 5-diaminobenzoic acid, a catalyst and an entrainer are added into a reactor to react under a protective atmosphere, and crude products are obtained and then extracted and distilled under reduced pressure to obtain grafted monomers.
The molar ratio of the polyethylene glycol to the 3, 5-diaminobenzoic acid is 1:1.32, the average molecular weight of the polyethylene glycol is 600, the catalyst is p-toluenesulfonic acid, the dosage of the catalyst is 4.8wt% of the polyethylene glycol, the entrainer is toluene, and the addition of the entrainer is 125 wt% of the polyethylene glycol.
The source of the polyethylene glycol is not particularly limited and can be purchased commercially, including but not limited to, polyethylene glycol from Shanghai, chemical technology, inc.
The strain solution comprises the mixture of nitrifying bacteria, denitrifying bacteria and bacillus subtilis, and the ratio of the viable bacteria to the bacterial strain is 1:1:1.25, wherein the nitrifying bacteria are nitrifying bacteria, the denitrifying bacteria are Pseudomonas mendocina, and the living bacterial amount of the strain solution is 10 10 CFU/g.
The slow-release film solution comprises the following components in percentage by mass: 8% of sodium alginate, 8% of gelatin, 5% of polyvinyl alcohol, 1.1% of methyl-pentapolyethylene glycol-succinimidyl acrylate, 1% of dihydroxypropyl PABA ethyl ester and the balance of water.
The slow release film solution is prepared by the following steps: mixing sodium alginate and water, dissolving in water bath at 50deg.C, adding gelatin, heating to 85deg.C to dissolve, adding polyvinyl alcohol under stirring to dissolve, adding methyl-pentapolyethylene glycol-succinimidyl acrylate and dihydroxypropyl PABA ethyl ester, and mixing uniformly to obtain the slow-release membrane solution.
The CAS number of methyl-pentapolyethylene glycol-succinimidyl acrylate is 1449390-12-8, the CAS number of dihydroxypropyl PABA ethyl ester is 58882-17-0, the polymerization degree of polyvinyl alcohol is 1799, the alcoholysis degree is 98-98%, and the average molecular weight is 44.05.
The source of the polyvinyl alcohol is not particularly limited and can be purchased commercially, including but not limited to, polyvinyl alcohol from Shanghai Hengfi Biotechnology Co., ltd, and the gelatin is industrial gelatin, including but not limited to, commercial gelatin from Shanghai county Fuyuan gelatin Co., ltd.
In order to reduce ammonia nitrogen and COD content in sewage, researchers in the field at present mainly add microbial agents into water, but the method can lead microorganisms to exist in a free form, so that the microorganisms are seriously lost and cannot be applied in the water for a long time, and thus the purification effect on sewage is limited.
In some embodiments, the thickener comprises at least one of xanthan gum, guar gum, gelatin, polyacrylamide.
Preferably, the thickener is a mixture of guar gum and polyacrylamide in a weight ratio of (0.3-0.7): 1, preferably 0.5:1.
The source of the guar is not particularly limited and may be purchased commercially, including but not limited to, guar from the chemical industry company of the river sea, any hilly city.
In some embodiments, the polyacrylamide is an anionic polyacrylamide.
Preferably, the molecular weight of the anionic polyacrylamide is 1500-3000.
The source of the anionic polyacrylamide is not particularly limited and can be purchased commercially, including but not limited to anionic polyacrylamide available from Henan Yanglin environmental protection technology Co., ltd, model DEFS and molecular weight 2000.
In some embodiments, the surfactant comprises an amphoteric surfactant and an anionic surfactant in a weight ratio of 1 (1-1.5).
In some embodiments, the amphoteric surfactant is cocamidopropyl betaine and the anionic surfactant is sodium dodecyl sulfate.
The cocoamidopropyl betaine has a CAS number of 61789-40-0 and sodium dodecyl sulfate has a CAS number of 151-21-3.
In some embodiments, the flocculant comprises at least one of aluminum sulfate, aluminum chloride, and polyaluminum chloride.
Preferably, the flocculant is a combination of aluminum sulfate and polyaluminum chloride in a weight ratio of (0.5-1): 1.
The slow release microsphere of the application has better effect on reducing ammonia nitrogen concentration and COD content, but has no obvious effect on the treatment of heavy metal ions, and the applicant finds that after a great deal of researches, the slow release microsphere is combined with a certain amount of specific surfactant, thickener and flocculant to prepare a water treatment agent, especially the surfactant is cocamidopropyl betaine and sodium dodecyl sulfate with the weight ratio of 1 (1-1.5), the thickener is a mixture of guar gum and polyacrylamide with the weight ratio of 0.3-0.7) 1, the synergistic treatment can be carried out on high ammonia nitrogen, COD, heavy metal ions and some small molecular harmful substances in the sewage, the excellent sewage purifying effect is realized, and the applicant considers that the possible reasons are that firstly guar gum and anionic polyacrylamide with a specific proportion can form flocculation glue, meanwhile, the amphoteric surfactant cocamidopropyl betaine is adsorbed on a molecular chain through self charge static electricity, and the anionic surfactant sodium dodecyl sulfate can promote the formation of the flocculation glue of guar gum, secondly the polyacrylamide and the oleamide can be associated with the oleamide propyl guar gum to form a three-dimensional structure, and the three-dimensional suspended particles can be combined with the alumina chloride to form a three-dimensional suspended particle with high-dimensional absorption effect, and the three-dimensional suspended particle can be reduced, the three-dimensional suspended particle can be combined with the space of the ammonia nitrogen can be formed, and the three-dimensional suspended particle can have high absorption effect can be formed, and the bridging effect ensures that suspended particles are connected and are easy to settle, thereby enhancing the sewage purification effect.
In some embodiments, the metal oxide comprises at least one of silica, titania, zinc oxide, antimony dioxide.
Preferably, the metal oxide is nano silicon dioxide, and the average particle size of the nano silicon dioxide is 15-30nm.
More preferably, the nanosilica has an average particle size of 20nm.
The source of the nano-silica is not particularly limited and can be purchased commercially, including but not limited to the nano-silica available from Yu mu (Ningbo) New Material Co., ltd., model YM-SiO2-20.
In some embodiments, the dispersant is methylpentanol or fatty alcohol polyoxyethylene ether.
Preferably, the dispersant is methylpentanol.
The second aspect of the invention provides a preparation method of a slow-release sewage treatment agent, which comprises the following steps: mixing a surfactant and a flocculating agent at 50-60 ℃, sequentially adding a metal oxide, a dispersing agent and a thickening agent under the stirring condition, cooling to below 30 ℃, adding slow-release microspheres, continuously stirring to obtain a semi-jelly, and drying and crushing the semi-jelly to obtain the slow-release sewage treatment agent.
Compared with the prior art, the invention has the following beneficial effects:
(1) According to the invention, the slow-release microsphere is prepared by adopting a special porous carrier to load the strain and then coating a layer of degradable slow-release film, and the pore structure of the porous carrier and the pores formed by the degradation of the slow-release film component in water are matched with each other so that the strain in the microsphere is slowly released, thus the long-acting purification effect on sewage is realized;
(2) The invention prepares the water treatment agent by combining and adding specific surfactants, thickening agents and flocculating agents into the slow-release microspheres, particularly the cocoamidopropyl betaine and sodium dodecyl sulfate with the weight ratio of 1 (1-1.5) and the mixture of guar gum and polyacrylamide with the weight ratio of 1 (0.3-0.7) are adopted as the surfactants, so that the synergistic treatment can be carried out on high ammonia nitrogen, COD, heavy metal ions and some small-molecular harmful substances in sewage, and the sewage purification effect is excellent.
Detailed Description
The technical solutions of the present invention will be clearly and completely described in connection with the embodiments, and it is obvious 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 invention without making any inventive effort, are intended to be within the scope of the invention.
Example 1
The slow-release sewage treatment agent comprises the following raw materials in parts by weight: 45 parts of slow release microspheres, 5 parts of thickener, 9 parts of surfactant, 25 parts of flocculant, 7 parts of metal oxide and 4 parts of dispersing agent.
The preparation of the slow release microsphere comprises the following steps:
(1) Dissolving diamine monomer and grafting monomer in N, N-dimethylformamide to obtain phase A, dispersing nonionic surfactant in liquid paraffin to obtain phase B, mixing the phase A and the phase B under stirring to form a nonaqueous emulsion system, adding dianhydride monomer to react for 4-6 hours to obtain polymer, adding a mixture of acetic anhydride and pyridine to perform chemical imidization to obtain precipitate, washing and drying the precipitate, performing thermal imidization to obtain modified polyimide polymer, and performing heat treatment on the modified polyimide polymer at 190 ℃ for 1 hour to obtain a modified polyimide porous carrier;
(2) Adding the modified polyimide porous carrier prepared in the step (1) into a strain solution, soaking for 2-3h, taking out, and drying to obtain microspheres loaded with strains;
(3) And (3) adding the strain-loaded microspheres obtained in the step (2) into a slow-release film solution, uniformly mixing, and drying to obtain the slow-release microspheres.
The molar ratio of diamine monomer to dianhydride monomer is 1:1.07, wherein the diamine monomer is 4,4' -diaminodiphenyl ether, the dianhydride monomer is pyromellitic dianhydride, the addition amount of the grafting monomer is 30wt% of the dianhydride monomer, the nonionic surfactant comprises span 85 and tween 80, and the weight ratio of the span 85 to the tween 80 is 1.8:1, the addition amount of the mixture of the acetic anhydride and the pyridine is 12 percent of the volume of the N, N-dimethylformamide, and the volume ratio of the acetic anhydride to the pyridine in the mixture of the acetic anhydride and the pyridine is 2:1.
The grafting monomer is obtained by the following steps: polyethylene glycol, 3, 5-diaminobenzoic acid, a catalyst and an entrainer are added into a reactor to react under a protective atmosphere, and crude products are obtained and then extracted and distilled under reduced pressure to obtain grafted monomers.
The molar ratio of polyethylene glycol to 3, 5-diaminobenzoic acid is 1:1.32, the average molecular weight of the polyethylene glycol is 600, the catalyst is p-toluenesulfonic acid, the dosage of the catalyst is 4.8wt% of the polyethylene glycol, the entrainer is toluene, and the addition of the entrainer is 125 wt% of the polyethylene glycol.
The source of the polyethylene glycol is not particularly limited and can be purchased commercially, including but not limited to, polyethylene glycol from Shanghai, chemical technology, inc.
The strain solution comprises the mixture of nitrifying bacteria, denitrifying bacteria and bacillus subtilis, and the ratio of the viable bacteria to the bacillus subtilis is 1:1:1.25, nitrifying bacteria are nitrifying bacteria, denitrifying bacteria are Pseudomonas mendocina, and the living bacterial amount of the bacterial strain solution is 10 10 CFU/g.
The slow-release film solution comprises the following components in percentage by mass: 8% of sodium alginate, 8% of gelatin, 5% of polyvinyl alcohol, 1.1% of methyl-pentapolyethylene glycol-succinimidyl acrylate, 1% of dihydroxypropyl PABA ethyl ester and the balance of water.
The slow release film solution is obtained by the following steps: mixing sodium alginate and water, dissolving in water bath at 50deg.C, adding gelatin, heating to 85deg.C to dissolve, adding polyvinyl alcohol under stirring to dissolve, adding methyl-pentapolyethylene glycol-succinimidyl acrylate and dihydroxypropyl PABA ethyl ester, and mixing uniformly to obtain the slow-release membrane solution.
The CAS number of methyl-pentapolyethylene glycol-succinimidyl acrylate is 1449390-12-8, the CAS number of dihydroxypropyl PABA ethyl ester is 58882-17-0, the polymerization degree of polyvinyl alcohol is 1799, the alcoholysis degree is 98-98%, and the average molecular weight is 44.05.
Polyvinyl alcohol was purchased from Shanghai Heng Fizea Biotech Co., ltd. Gelatin was an industrial gelatin, and was purchased from Shangshui county Fuyuan gelatin Co., ltd.
The thickener is a mixture of guar gum and polyacrylamide, and the weight ratio of the guar gum to the polyacrylamide is 0.5:1.
Guar gum is purchased from Jianghai chemical industry Co., ltd, and polyacrylamide is anionic polyacrylamide, and is purchased from Henan Yanglin environmental protection technology Co., ltd, and the model is DEFS, and the molecular weight is 2000.
The surfactant comprises an amphoteric surfactant and an anionic surfactant, and the weight ratio of the amphoteric surfactant to the anionic surfactant is 1:1.25, wherein the amphoteric surfactant is cocamidopropyl betaine, and the anionic surfactant is sodium dodecyl sulfate.
The flocculant is a combination of aluminum sulfate and polyaluminum chloride, and the weight ratio of the aluminum sulfate to the polyaluminum chloride is 0.75:1.
The metal oxide is nano silicon dioxide with the average grain diameter of 20nm, and the nano silicon dioxide is purchased from Yumu (Ningbo) new material Co., ltd, and the model is YM-SiO2-20.
The dispersing agent is methyl amyl alcohol.
The preparation method of the slow-release sewage treatment agent comprises the following steps: mixing a surfactant and a flocculating agent at 55 ℃, sequentially adding a metal oxide, a dispersing agent and a thickening agent under the stirring condition, cooling to below 30 ℃, adding slow-release microspheres, continuously stirring to obtain a semi-gelatinous substance, and drying and crushing the semi-gelatinous substance to obtain the slow-release sewage treatment agent.
Example 2
The slow-release sewage treatment agent comprises the following raw materials in parts by weight: 40 parts of slow release microspheres, 4 parts of thickener, 8 parts of surfactant, 20 parts of flocculant, 5 parts of metal oxide and 3 parts of dispersing agent.
The preparation of the slow release microsphere comprises the following steps:
(1) Dissolving diamine monomer and grafting monomer in N, N-dimethylformamide to obtain phase A, dispersing nonionic surfactant in liquid paraffin to obtain phase B, mixing the phase A and the phase B under stirring to form a nonaqueous emulsion system, adding dianhydride monomer to react for 4-6 hours to obtain polymer, adding a mixture of acetic anhydride and pyridine to perform chemical imidization to obtain precipitate, washing and drying the precipitate, performing thermal imidization to obtain modified polyimide polymer, and performing heat treatment on the modified polyimide polymer at 190 ℃ for 1 hour to obtain a modified polyimide porous carrier;
(2) Adding the modified polyimide porous carrier prepared in the step (1) into a strain solution, soaking for 2-3h, taking out, and drying to obtain microspheres loaded with strains;
(3) And (3) adding the strain-loaded microspheres obtained in the step (2) into a slow-release film solution, uniformly mixing, and drying to obtain the slow-release microspheres.
The molar ratio of diamine monomer to dianhydride monomer is 1:1.07, wherein the diamine monomer is 4,4' -diaminodiphenyl ether, the dianhydride monomer is pyromellitic dianhydride, the addition amount of the grafting monomer is 30wt% of the dianhydride monomer, the nonionic surfactant comprises span 85 and tween 80, and the weight ratio of the span 85 to the tween 80 is 1.8:1, the addition amount of the mixture of the acetic anhydride and the pyridine is 12 percent of the volume of the N, N-dimethylformamide, and the volume ratio of the acetic anhydride to the pyridine in the mixture of the acetic anhydride and the pyridine is 2:1.
The grafting monomer is obtained by the following steps: polyethylene glycol, 3, 5-diaminobenzoic acid, a catalyst and an entrainer are added into a reactor to react under a protective atmosphere, and crude products are obtained and then extracted and distilled under reduced pressure to obtain grafted monomers.
The molar ratio of polyethylene glycol to 3, 5-diaminobenzoic acid is 1:1.32, the average molecular weight of the polyethylene glycol is 600, the catalyst is p-toluenesulfonic acid, the dosage of the catalyst is 4.8wt% of the polyethylene glycol, the entrainer is toluene, and the addition of the entrainer is 125 wt% of the polyethylene glycol.
The source of the polyethylene glycol is not particularly limited and can be purchased commercially, including but not limited to, polyethylene glycol from Shanghai, chemical technology, inc.
The strain solution comprises the mixture of nitrifying bacteria, denitrifying bacteria and bacillus subtilis, and the ratio of the viable bacteria to the bacillus subtilis is 1:1:1.25, nitrifying bacteria are nitrifying bacteria, denitrifying bacteria are Pseudomonas mendocina, and the living bacterial amount of the bacterial strain solution is 10 10 CFU/g.
The slow-release film solution comprises the following components in percentage by mass: 8% of sodium alginate, 8% of gelatin, 5% of polyvinyl alcohol, 1.1% of methyl-pentapolyethylene glycol-succinimidyl acrylate, 1% of dihydroxypropyl PABA ethyl ester and the balance of water.
The slow release film solution is obtained by the following steps: mixing sodium alginate and water, dissolving in water bath at 50deg.C, adding gelatin, heating to 85deg.C to dissolve, adding polyvinyl alcohol under stirring to dissolve, adding methyl-pentapolyethylene glycol-succinimidyl acrylate and dihydroxypropyl PABA ethyl ester, and mixing uniformly to obtain the slow-release membrane solution.
The CAS number of methyl-pentapolyethylene glycol-succinimidyl acrylate is 1449390-12-8, the CAS number of dihydroxypropyl PABA ethyl ester is 58882-17-0, the polymerization degree of polyvinyl alcohol is 1799, the alcoholysis degree is 98-98%, and the average molecular weight is 44.05.
Polyvinyl alcohol was purchased from Shanghai Heng Fizea Biotech Co., ltd. Gelatin was an industrial gelatin, and was purchased from Shangshui county Fuyuan gelatin Co., ltd.
The thickener is a mixture of guar gum and polyacrylamide, and the weight ratio of the guar gum to the polyacrylamide is 0.3:1.
Guar gum is purchased from Jianghai chemical industry Co., ltd, and polyacrylamide is anionic polyacrylamide, and is purchased from Henan Yanglin environmental protection technology Co., ltd, and the model is DEFS, and the molecular weight is 2000.
The surfactant comprises an amphoteric surfactant and an anionic surfactant, and the weight ratio of the amphoteric surfactant to the anionic surfactant is 1:1, wherein the amphoteric surfactant is cocamidopropyl betaine, and the anionic surfactant is sodium dodecyl sulfate.
The flocculant is a combination of aluminum sulfate and polyaluminum chloride, and the weight ratio of the aluminum sulfate to the polyaluminum chloride is 0.5:1.
The metal oxide is nano silicon dioxide with the average grain diameter of 20nm, and the nano silicon dioxide is purchased from Yumu (Ningbo) new material Co., ltd, and the model is YM-SiO2-20.
The dispersing agent is methyl amyl alcohol.
The preparation method of the slow-release sewage treatment agent comprises the following steps: mixing a surfactant and a flocculating agent at 55 ℃, sequentially adding a metal oxide, a dispersing agent and a thickening agent under the stirring condition, cooling to below 30 ℃, adding slow-release microspheres, continuously stirring to obtain a semi-gelatinous substance, and drying and crushing the semi-gelatinous substance to obtain the slow-release sewage treatment agent.
Example 3
The slow-release sewage treatment agent comprises the following raw materials in parts by weight: 50 parts of slow release microspheres, 6 parts of thickener, 10 parts of surfactant, 30 parts of flocculant, 10 parts of metal oxide and 5 parts of dispersing agent.
The preparation of the slow release microsphere comprises the following steps:
(1) Dissolving diamine monomer and grafting monomer in N, N-dimethylformamide to obtain phase A, dispersing nonionic surfactant in liquid paraffin to obtain phase B, mixing the phase A and the phase B under stirring to form a nonaqueous emulsion system, adding dianhydride monomer to react for 4-6 hours to obtain polymer, adding a mixture of acetic anhydride and pyridine to perform chemical imidization to obtain precipitate, washing and drying the precipitate, performing thermal imidization to obtain modified polyimide polymer, and performing heat treatment on the modified polyimide polymer at 190 ℃ for 1 hour to obtain a modified polyimide porous carrier;
(2) Adding the modified polyimide porous carrier prepared in the step (1) into a strain solution, soaking for 2-3h, taking out, and drying to obtain microspheres loaded with strains;
(3) And (3) adding the strain-loaded microspheres obtained in the step (2) into a slow-release film solution, uniformly mixing, and drying to obtain the slow-release microspheres.
The molar ratio of diamine monomer to dianhydride monomer is 1:1.07, wherein the diamine monomer is 4,4' -diaminodiphenyl ether, the dianhydride monomer is pyromellitic dianhydride, the addition amount of the grafting monomer is 30wt% of the dianhydride monomer, the nonionic surfactant comprises span 85 and tween 80, and the weight ratio of the span 85 to the tween 80 is 1.8:1, the addition amount of the mixture of the acetic anhydride and the pyridine is 12 percent of the volume of the N, N-dimethylformamide, and the volume ratio of the acetic anhydride to the pyridine in the mixture of the acetic anhydride and the pyridine is 2:1.
The grafting monomer is obtained by the following steps: polyethylene glycol, 3, 5-diaminobenzoic acid, a catalyst and an entrainer are added into a reactor to react under a protective atmosphere, and crude products are obtained and then extracted and distilled under reduced pressure to obtain grafted monomers.
The molar ratio of polyethylene glycol to 3, 5-diaminobenzoic acid is 1:1.32, the average molecular weight of the polyethylene glycol is 600, the catalyst is p-toluenesulfonic acid, the dosage of the catalyst is 4.8wt% of the polyethylene glycol, the entrainer is toluene, and the addition of the entrainer is 125 wt% of the polyethylene glycol.
The source of the polyethylene glycol is not particularly limited and can be purchased commercially, including but not limited to, polyethylene glycol from Shanghai, chemical technology, inc.
The strain solution comprises the mixture of nitrifying bacteria, denitrifying bacteria and bacillus subtilis, and the ratio of the viable bacteria to the bacillus subtilis is 1:1:1.25, nitrifying bacteria are nitrifying bacteria, denitrifying bacteria are Pseudomonas mendocina, and the living bacterial amount of the bacterial strain solution is 10 10 CFU/g.
The slow-release film solution comprises the following components in percentage by mass: 8% of sodium alginate, 8% of gelatin, 5% of polyvinyl alcohol, 1.1% of methyl-pentapolyethylene glycol-succinimidyl acrylate, 1% of dihydroxypropyl PABA ethyl ester and the balance of water.
The slow release film solution is obtained by the following steps: mixing sodium alginate and water, dissolving in water bath at 50deg.C, adding gelatin, heating to 85deg.C to dissolve, adding polyvinyl alcohol under stirring to dissolve, adding methyl-pentapolyethylene glycol-succinimidyl acrylate and dihydroxypropyl PABA ethyl ester, and mixing uniformly to obtain the slow-release membrane solution.
The CAS number of methyl-pentapolyethylene glycol-succinimidyl acrylate is 1449390-12-8, the CAS number of dihydroxypropyl PABA ethyl ester is 58882-17-0, the polymerization degree of polyvinyl alcohol is 1799, the alcoholysis degree is 98-98%, and the average molecular weight is 44.05.
Polyvinyl alcohol was purchased from Shanghai Heng Fizea Biotech Co., ltd. Gelatin was an industrial gelatin, and was purchased from Shangshui county Fuyuan gelatin Co., ltd.
The thickener is a mixture of guar gum and polyacrylamide, and the weight ratio of the guar gum to the polyacrylamide is 0.3:1.
Guar gum is purchased from Jianghai chemical industry Co., ltd, and polyacrylamide is anionic polyacrylamide, and is purchased from Henan Yanglin environmental protection technology Co., ltd, and the model is DEFS, and the molecular weight is 2000.
The surfactant comprises an amphoteric surfactant and an anionic surfactant, and the weight ratio of the amphoteric surfactant to the anionic surfactant is 1:1, wherein the amphoteric surfactant is cocamidopropyl betaine, and the anionic surfactant is sodium dodecyl sulfate.
The flocculant is a combination of aluminum sulfate and polyaluminum chloride, and the weight ratio of the aluminum sulfate to the polyaluminum chloride is 0.5:1.
The metal oxide is nano silicon dioxide with the average grain diameter of 20nm, and the nano silicon dioxide is purchased from Yumu (Ningbo) new material Co., ltd, and the model is YM-SiO2-20.
The dispersing agent is methyl amyl alcohol.
The preparation method of the slow-release sewage treatment agent comprises the following steps: mixing a surfactant and a flocculating agent at 55 ℃, sequentially adding a metal oxide, a dispersing agent and a thickening agent under the stirring condition, cooling to below 30 ℃, adding slow-release microspheres, continuously stirring to obtain a semi-gelatinous substance, and drying and crushing the semi-gelatinous substance to obtain the slow-release sewage treatment agent.
Example 4
The embodiment provides a slow-release sewage treatment agent and a preparation method thereof, and the specific implementation mode is the same as the embodiment 1, except that guar gum is not included in the thickener.
Example 5
The present example provides a slow-release sewage treatment agent and a preparation method thereof, and a specific embodiment is the same as example 1, except that the thickener does not include anionic polyacrylamide.
Example 6
The present example provides a slow-release sewage treatment agent and a preparation method thereof, and a specific embodiment is the same as example 1, except that the surfactant does not include sodium dodecyl sulfate.
Evaluation of Performance
1. Sewage purification effect
The initial concentration of ammonia nitrogen in wastewater of a certain factory is 300mg/L, the initial concentration of COD is 1000mg/L, and the concentration of heavy metal ions is respectively as follows: cu 2+30mg/L,Cr6+85mg/L,Zn2+40mg/L,Ni2+ mg/L, adjusting the pH of the wastewater to be neutral, and then taking 6 parts of the wastewater with the same amount, and respectively adding the water treatment agents of examples 1-6 with the addition amount of 20g/L.
Sampling and measuring ammonia nitrogen concentration and COD concentration after 24h and 3 days, respectively measuring the concentration of each heavy metal ion after 24h by an atomic absorption spectrophotometer, and calculating the ion adsorption rate, wherein the ion adsorption rate has the following calculation formula: ion adsorption ratio (%) = (initial ion concentration-ion concentration after treatment)/initial ion concentration×100%.
The test results are shown in Table 1.
TABLE 1
As can be seen from the data in table 1, the water treatment agents of examples 1 to 3 are excellent in reducing ammonia nitrogen and COD concentration and heavy metal ion adsorption effect, and according to the data, the reduction of ammonia nitrogen concentration and COD concentration is more obvious with the extension of treatment time, and the water treatment agent is proved to have better slow release performance; in examples 4 and 5, the removal effect on ammonia nitrogen and COD is slightly poor due to the change of the components of the thickener, and the adsorption effect on various heavy metal ions is obviously deteriorated to different degrees; example 6 has a slightly inferior ammonia nitrogen and COD removal effect due to the change of the components of the surfactant, and also has a remarkably inferior adsorption effect on various heavy metal ions.
Finally, it should be noted that the above-mentioned embodiments are only for illustrating the technical solution of the present invention, and not for limiting the same, and although the present invention has been described in detail with reference to examples, it should be understood by those skilled in the art that modifications and equivalents may be made to the technical solution of the present invention without departing from the spirit and scope of the technical solution of the present invention, and all such modifications and equivalents are intended to be encompassed in the scope of the claims of the present invention.

Claims (5)

1. The slow-release sewage treatment agent is characterized by comprising the following raw materials in parts by weight: 40-50 parts of slow release microspheres, 4-6 parts of thickening agent, 8-10 parts of surfactant, 20-30 parts of flocculating agent, 5-10 parts of metal oxide and 3-5 parts of dispersing agent;
the preparation of the slow release microsphere comprises the following steps:
(1) Dissolving diamine monomer and grafting monomer in N, N-dimethylformamide to obtain a phase A, dispersing nonionic surfactant in liquid paraffin to obtain a phase B, mixing the phase A and the phase B under stirring to form a nonaqueous emulsion system, adding dianhydride monomer to react for 4-6 hours to obtain a polymer, adding a mixture of acetic anhydride and pyridine to perform chemical imidization to obtain a precipitate, washing and drying the precipitate, performing thermal imidization to obtain a modified polyimide polymer, and performing heat treatment on the modified polyimide polymer to obtain a modified polyimide porous carrier;
(2) Adding the modified polyimide porous carrier prepared in the step (1) into a strain solution, soaking for 2-3h, taking out, and drying to obtain microspheres loaded with strains;
(3) Adding the strain-loaded microspheres obtained in the step (2) into a slow-release film solution, uniformly mixing, and drying to obtain slow-release microspheres;
The molar ratio of the diamine monomer to the dianhydride monomer is 1:1.07, wherein the diamine monomer is 4,4' -diaminodiphenyl ether, the dianhydride monomer is pyromellitic dianhydride, the addition amount of the grafting monomer is 30wt% of the dianhydride monomer, the nonionic surfactant comprises span 85 and tween 80, and the weight ratio of the span 85 to the tween 80 is 1.8:1, the addition amount of the mixture of acetic anhydride and pyridine is 12% of the volume of N, N-dimethylformamide, and the volume ratio of the acetic anhydride to the pyridine in the mixture of the acetic anhydride and the pyridine is 2:1;
the slow-release film solution comprises the following components in percentage by mass: 8% of sodium alginate, 8% of gelatin, 5% of polyvinyl alcohol, 1.1% of methyl-pentapolyethylene glycol-succinimidyl acrylate, 1% of dihydroxypropyl PABA ethyl ester and the balance of water;
The thickener is a mixture of guar gum and polyacrylamide, and the weight ratio of the guar gum to the polyacrylamide is (0.3-0.7) 1;
The surfactant comprises an amphoteric surfactant and an anionic surfactant, and the weight ratio of the amphoteric surfactant to the anionic surfactant is 1 (1-1.5);
the amphoteric surfactant is cocamidopropyl betaine, and the anionic surfactant is sodium dodecyl sulfate;
the flocculant comprises at least one of aluminum sulfate, aluminum chloride and polyaluminum chloride.
2. The slow-release sewage treatment agent according to claim 1, wherein the polyacrylamide is anionic polyacrylamide.
3. The slow release type sewage treatment agent according to claim 1, wherein the metal oxide comprises at least one of silica, titanium dioxide, zinc oxide and antimony dioxide.
4. The slow-release sewage treatment agent according to claim 1, wherein the dispersing agent is methylpentanol or fatty alcohol polyoxyethylene ether.
5. A method for preparing the slow-release sewage treatment agent according to any one of claims 1 to 4, comprising the steps of: mixing a surfactant and a flocculating agent at 50-60 ℃, sequentially adding a metal oxide, a dispersing agent and a thickening agent under the stirring condition, cooling to below 30 ℃, adding slow-release microspheres, continuously stirring to obtain a semi-jelly, and drying and crushing the semi-jelly to obtain the slow-release sewage treatment agent.
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