CN111689589A - Sewage treatment agent - Google Patents

Sewage treatment agent Download PDF

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Publication number
CN111689589A
CN111689589A CN202010467150.9A CN202010467150A CN111689589A CN 111689589 A CN111689589 A CN 111689589A CN 202010467150 A CN202010467150 A CN 202010467150A CN 111689589 A CN111689589 A CN 111689589A
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citric acid
treatment agent
modified sisal
sewage treatment
sisal fiber
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张益昌
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Nanjing Aoboer Environmental Protection Equipment Co ltd
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Nanjing Aoboer Environmental Protection Equipment Co ltd
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Priority to CN202010467150.9A priority Critical patent/CN111689589A/en
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F5/00Softening water; Preventing scale; Adding scale preventatives or scale removers to water, e.g. adding sequestering agents
    • C02F5/08Treatment of water with complexing chemicals or other solubilising agents for softening, scale prevention or scale removal, e.g. adding sequestering agents
    • C02F5/10Treatment of water with complexing chemicals or other solubilising agents for softening, scale prevention or scale removal, e.g. adding sequestering agents using organic substances
    • C02F5/14Treatment of water with complexing chemicals or other solubilising agents for softening, scale prevention or scale removal, e.g. adding sequestering agents using organic substances containing phosphorus
    • 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
    • B01J20/22Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material
    • B01J20/24Naturally occurring macromolecular compounds, e.g. humic acids or their derivatives
    • 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
    • B01J20/28014Solid 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 form
    • B01J20/28016Particle form
    • B01J20/28021Hollow particles, e.g. hollow spheres, microspheres or cenospheres
    • 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
    • C02F1/285Treatment of water, waste water, or sewage by sorption using synthetic organic sorbents
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J2220/00Aspects relating to sorbent materials
    • B01J2220/40Aspects relating to the composition of sorbent or filter aid materials
    • B01J2220/48Sorbents characterised by the starting material used for their preparation
    • B01J2220/4812Sorbents characterised by the starting material used for their preparation the starting material being of organic character
    • B01J2220/4825Polysaccharides or cellulose materials, e.g. starch, chitin, sawdust, wood, straw, cotton
    • 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
    • C02F2101/206Manganese or manganese compounds
    • 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
    • C02F2101/22Chromium or chromium compounds, e.g. chromates
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2303/00Specific treatment goals
    • C02F2303/08Corrosion inhibition

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

Abstract

The invention discloses a sewage treatment agent, which comprises the following raw materials: organic carboxylic acid, modified sisal fiber porous microspheres, polyamino acid, starch xanthate and amino trimethylene phosphonic acid; the preparation method of the sewage treatment agent comprises the following steps: preparing modified sisal fiber porous microspheres; adding organic carboxylic acid and polyamino acid into the citric acid modified sisal fiber cross-linked chitosan porous microspheres, fully mixing uniformly, adding starch xanthate and amino trimethylene phosphonic acid, and fully mixing uniformly again to obtain a sewage treatment agent; the sewage treatment agent disclosed by the invention can capture various metal ions in a water body by compounding the raw materials and exerting a synergistic effect, and also has obvious corrosion and scale inhibition effects, so that the scaling and corrosion of a system can be effectively reduced, and the production cost is reduced; the treated sewage can reach the discharge standard, and the floc strength is high and the hydrophobic property is good; the treated water has no secondary pollution and other problems.

Description

Sewage treatment agent
Technical Field
The invention relates to the technical field of sewage treatment, in particular to a sewage treatment agent.
Background
China is a country with shortage of water resources, and the water resources are distributed seriously unevenly, so that the problem of how to relieve the problems of water resource shortage, pollution and the like becomes an unbearable problem. In order to solve the problem of water shortage, pollution control is gradually one of the basic principles that China must insist for a long time except for source-opening throttling and comprehensive utilization.
At present, the methods for treating heavy metal wastewater are commonly classified into three types: the first kind is a method for removing heavy metal ions in the wastewater by chemical reaction, which comprises a neutralization precipitation method, a sulfide precipitation method, a ferrite coprecipitation method, a chemical reduction method, an electrochemical reduction method, a high-molecular heavy metal collector method and the like; the second type is a method for adsorbing, concentrating and separating heavy metals in wastewater under the condition of not changing the chemical forms of the heavy metals, and comprises adsorption, solvent extraction, evaporation and solidification, ion exchange, membrane separation and the like. The third category is a method for removing heavy metals in wastewater by the flocculation, absorption, accumulation, enrichment and the like of microorganisms or plants, wherein the method comprises biological flocculation, biochemical methods, plant ecological restoration and the like.
However, the existing heavy metal wastewater treatment agent has some problems, such as high treatment cost, secondary pollution, poor treatment effect and the like.
Disclosure of Invention
The invention aims to provide a sewage treatment agent, which solves the problems of high treatment cost, secondary pollution and poor treatment effect of heavy metal wastewater treatment agents in the prior art.
In order to achieve the purpose, the invention provides the following technical scheme:
on one hand, the invention provides a sewage treatment agent, which comprises the following raw materials in parts by weight: 5-10 parts of organic carboxylic acid, 20-30 parts of modified sisal fiber porous microspheres, 5-10 parts of polyamino acid, 5-10 parts of starch xanthate and 1-5 parts of amino trimethylene phosphonic acid.
Further, the modified sisal fiber porous microspheres are citric acid modified sisal fiber crosslinked chitosan porous microspheres obtained by carrying out citric acid modification, activating agent activation and chitosan crosslinking on sisal fibers.
Further, the organic carboxylic acid is one or more of lactic acid, hydroxybutyric acid, salicylic acid and tartaric acid.
Further, the polyamino acid is polyglycine, polyasparagine or polyglutamic acid.
In another aspect, the present invention provides a method for preparing a wastewater treatment agent, comprising:
preparing modified sisal fiber porous microspheres:
dissolving sisal fibers in citric acid, adding a catalyst, carrying out hydrothermal reaction in a high-pressure kettle, centrifuging after the reaction is finished, taking a lower-layer precipitate, washing and drying to obtain citric acid modified sisal fibers;
dissolving the citric acid modified sisal fibers in water, and then adding an activating agent for activation to obtain an activated citric acid modified sisal fiber aqueous solution;
adding the activated citric acid modified sisal fiber aqueous solution into a chitosan aqueous solution, uniformly stirring, standing and aging to obtain citric acid modified sisal fiber crosslinked chitosan hydrogel;
freeze-drying the citric acid modified sisal fiber cross-linked chitosan hydrogel to obtain citric acid modified sisal fiber cross-linked chitosan porous microspheres;
mixing: and adding organic carboxylic acid and polyamino acid into the citric acid modified sisal fiber crosslinked chitosan porous microspheres, fully mixing uniformly, adding starch xanthate and amino trimethylene phosphonic acid, and fully mixing uniformly again to obtain the sewage treatment agent.
Further, the mole ratio of the sisal fibers to the citric acid to the catalyst is 1: 4-8: 0.01-0.2; the catalyst is sodium hypophosphite.
Furthermore, the hydrothermal reaction temperature of the high-pressure kettle is 100-140 ℃, and the reaction time is 4-6 h.
Further, the activating agent is 1- (3-dimethylaminopropyl) -3-ethylcarbodiimide hydrochloride or N-hydroxysuccinimide; the activation time is 10-15 min.
Further, the mass ratio of the activated citric acid modified sisal fibers to the chitosan is 1: 2-5.
Further, the freeze drying system is liquid nitrogen/ethanol, the temperature is-60 to-100 ℃, and the time is 24 to 48 hours.
Starch xanthate (1SX) is a heavy metal high-efficiency remover and can generate a complex with a plurality of heavy metal ions.
The peptide bond on the main chain of the polyamino acid is easy to be broken by the action of microorganisms, fungi and the like, and the final degradation products are ammonia, carbon dioxide and water which are harmless to the environment, so the polyamino acid is an environment-friendly chemical with good biodegradability. The polyamino acid is a water-soluble polymer, is a novel green water treatment agent, and has the characteristics of no phosphorus, no toxicity, no public nuisance and complete biodegradation. Has strong chelating ability to ions, has double effects of corrosion inhibition and scale inhibition, and has good scale inhibition effect on scale forming salts such as calcium carbonate, calcium sulfate, barium sulfate, calcium phosphate and the like. The polyamino acid can replace phosphorus-containing water treatment agents so as to avoid eutrophication of water bodies and discharge secondary pollution. As a water treatment agent, it has the main functions of scale inhibition and/or dispersion and corrosion inhibition. The scale inhibitor is particularly suitable for inhibiting the formation of calcium carbonate scale, calcium sulfate scale, barium sulfate scale and calcium phosphate scale in cooling water, boiler water and reverse osmosis treatment.
The organic carboxylic acid is one or more of lactic acid, hydroxybutyric acid, tartaric acid and salicylic acid, is a linear compound containing hydroxyl, has double properties of alcohol and carboxylic acid, and is ionized after being dissolved in water to generate a molecular chain with negative charges. The molecular chains with negative charges can react with calcium scale, magnesium scale and the like on the metal surface to form compounds capable of being dissolved in water, so that the compounds can be stripped from the metal surface, and hydrogen bonds of hydroxyl groups can form a layer of compact film with the metal surface, and the compact film is adsorbed on the metal surface, is smooth, has strong corrosion resistance, is difficult to adhere to dirt, has a dirt resisting effect, and prevents corrosion or scaling of the metal surface. Meanwhile, the organic carboxylic acid contains hydroxyl and carboxyl, so that a hydrophilic chelate can be formed with metal cations through coordination bonds, the growth of iron-oxidizing bacteria is obviously inhibited, and the bactericidal effect is achieved.
The amino trimethylene phosphonic acid has good chelation, and the amino trimethylene phosphonic acid has stable chemical property in water, is not easy to hydrolyze, and can form a stable complex with various metal ions.
The modified sisal fiber porous microspheres (citric acid modified sisal fiber cross-linked chitosan porous microspheres) can be regenerated after absorbing heavy metals, and still have strong adsorption capacity after being regenerated; the modified sisal fiber porous microspheres (citric acid modified sisal fiber cross-linked chitosan porous microspheres) have carboxylate ions, the carboxylate ions are easily combined with metal ions through ionic bonds, and the combination force between the two is strong; the modified sisal fiber porous microspheres (citric acid modified sisal fiber crosslinked chitosan porous microspheres) are suitable for adsorbing heavy metal ions in an aqueous solution, and metal ions capable of combining with carboxylate radicals to form ionic bonds belong to the adsorption category.
Compared with the prior art, the invention has the beneficial effects that:
the sewage treatment agent disclosed by the invention can capture various metal ions in a water body by compounding the raw materials and exerting a synergistic effect, and also has obvious corrosion and scale inhibition effects, so that the scaling and corrosion of a system can be effectively reduced, and the production cost is reduced;
secondly, the sewage treatment agent of the invention is used for treating cadmium (Cd) in heavy metal sewage2+) Lead (Pb)2+) Copper (Cu)2+) Nickel (Ni)2 +) Zinc (Zn), zinc (Zn)2+) The removal rates are respectively more than 99.9%, more than 99.4%, more than 99.3%, more than 99.8% and more than 99.3%, the removal rates of chromium, manganese and mercury in heavy metal sewage are respectively more than 99.7%, more than 99.9% and more than 99.9%, and the treatment effect is good;
the sewage treatment agent has stable performance, good precipitation effect, good effluent quality and low treatment cost; after the medicament is added into sewage, suspended matters are immediately flocculated and quickly precipitated; the treated sewage can reach the discharge standard, and the floc strength is high and the hydrophobic property is good;
the sewage treatment agent disclosed by the invention has the advantages of high purity, no toxicity, no influence on operators, no secondary pollution of treated water and the like.
Detailed Description
The technical solutions in the embodiments of the present invention will be clearly and completely described below with reference to the embodiments of the present invention, and it is obvious that the described embodiments are only a part of the embodiments of the present invention, and not all of the embodiments. All other embodiments, which can be derived by a person skilled in the art from the embodiments given herein without making any creative effort, shall fall within the protection scope of the present invention.
Example 1:
a sewage treatment agent comprises the following raw materials in parts by weight: 5 parts of lactic acid, 20 parts of modified sisal fiber porous microspheres, 5 parts of polyglycine, 5 parts of starch xanthate and 1 part of amino trimethylene phosphonic acid; the modified sisal fiber porous microspheres are citric acid modified sisal fiber crosslinked chitosan porous microspheres obtained by carrying out citric acid modification, 1- (3-dimethylaminopropyl) -3-ethylcarbodiimide hydrochloride activation and chitosan crosslinking on sisal fibers.
A preparation method of a sewage treatment agent comprises the following steps:
preparing modified sisal fiber porous microspheres:
dissolving sisal fibers in citric acid, adding sodium hypophosphite, carrying out hydrothermal reaction in an autoclave at the hydrothermal reaction temperature of 100 ℃ for 4h, centrifuging after the reaction is finished, taking the lower layer of precipitate, washing and drying to obtain citric acid modified sisal fibers, wherein the molar ratio of the sisal fibers to the citric acid to the sodium hypophosphite is 1:4: 0.01;
dissolving the citric acid modified sisal fibers in water, and then adding 1- (3-dimethylaminopropyl) -3-ethylcarbodiimide hydrochloride for activation for 10min to obtain an activated citric acid modified sisal fiber aqueous solution;
adding the activated citric acid modified sisal fiber aqueous solution into a chitosan aqueous solution, wherein the mass ratio of the activated citric acid modified sisal fibers to the chitosan is 1:2, uniformly stirring, standing and aging to obtain citric acid modified sisal fiber crosslinked chitosan hydrogel;
freeze-drying the citric acid modified sisal fiber cross-linked chitosan hydrogel at-60 ℃ for 24 hours by using liquid nitrogen/ethanol as a freeze-drying system to obtain the citric acid modified sisal fiber cross-linked chitosan porous microspheres;
mixing: and adding lactic acid and polyglycine into the citric acid modified sisal fiber cross-linked chitosan porous microspheres, fully mixing uniformly, adding starch xanthate and amino trimethylene phosphonic acid, and fully mixing uniformly again to obtain the sewage treatment agent.
Example 2:
a sewage treatment agent comprises the following raw materials in parts by weight: 6 parts of hydroxybutyric acid, 22 parts of modified sisal fiber porous microspheres, 6 parts of polyasparagine, 6 parts of starch xanthate and 2 parts of amino trimethylene phosphonic acid; the modified sisal fiber porous microspheres are citric acid modified sisal fiber crosslinked chitosan porous microspheres obtained by carrying out citric acid modification, N-hydroxysuccinimide activation and chitosan crosslinking on sisal fibers.
A preparation method of a sewage treatment agent comprises the following steps:
preparing modified sisal fiber porous microspheres:
dissolving sisal fibers in citric acid, adding sodium hypophosphite, carrying out hydrothermal reaction in an autoclave at the hydrothermal reaction temperature of 110 ℃ for 4.5 hours, centrifuging after the reaction is finished, taking the lower layer of precipitate, washing and drying to obtain citric acid modified sisal fibers, wherein the molar ratio of the sisal fibers to the citric acid to the sodium hypophosphite is 1:5: 0.05;
dissolving the citric acid modified sisal fibers in water, and then adding N-hydroxysuccinimide for activation for 11min to obtain an activated citric acid modified sisal fiber aqueous solution;
adding the activated citric acid modified sisal fiber aqueous solution into a chitosan aqueous solution, wherein the mass ratio of the activated citric acid modified sisal fibers to the chitosan is 1:2.5, uniformly stirring, standing and aging to obtain citric acid modified sisal fiber crosslinked chitosan hydrogel;
freeze-drying the citric acid modified sisal fiber cross-linked chitosan hydrogel at-70 ℃ for 30 hours by using liquid nitrogen/ethanol as a freeze-drying system to obtain the citric acid modified sisal fiber cross-linked chitosan porous microspheres;
mixing: and adding hydroxybutyric acid and polyasparagine into the citric acid modified sisal fiber crosslinked chitosan porous microspheres, fully mixing uniformly, adding starch xanthate and amino trimethylene phosphonic acid, and fully mixing uniformly again to obtain the sewage treatment agent.
Example 3:
a sewage treatment agent comprises the following raw materials in parts by weight: 7.5 parts of salicylic acid, 25 parts of modified sisal fiber porous microspheres, 7.5 parts of polyglutamic acid, 7.5 parts of starch xanthate and 3 parts of amino trimethylene phosphonic acid; the modified sisal fiber porous microspheres are citric acid modified sisal fiber crosslinked chitosan porous microspheres obtained by carrying out citric acid modification, 1- (3-dimethylaminopropyl) -3-ethylcarbodiimide hydrochloride activation and chitosan crosslinking on sisal fibers.
A preparation method of a sewage treatment agent comprises the following steps:
preparing modified sisal fiber porous microspheres:
dissolving sisal fibers in citric acid, adding sodium hypophosphite, performing hydrothermal reaction in an autoclave at the hydrothermal reaction temperature of 120 ℃ for 5 hours, centrifuging after the reaction is finished, taking the lower layer of precipitate, washing and drying to obtain citric acid modified sisal fibers, wherein the molar ratio of the sisal fibers to the citric acid to the sodium hypophosphite is 1:6: 0.1;
dissolving the citric acid modified sisal fibers in water, and then adding 1- (3-dimethylaminopropyl) -3-ethylcarbodiimide hydrochloride for activation for 12.5min to obtain an activated citric acid modified sisal fiber aqueous solution; the activating agent is 1- (3-dimethylaminopropyl) -3-ethylcarbodiimide hydrochloride or N-hydroxysuccinimide;
adding the activated citric acid modified sisal fiber aqueous solution into a chitosan aqueous solution, wherein the mass ratio of the activated citric acid modified sisal fibers to the chitosan is 1:3.5, uniformly stirring, standing and aging to obtain citric acid modified sisal fiber crosslinked chitosan hydrogel;
freeze-drying the citric acid modified sisal fiber cross-linked chitosan hydrogel at-80 ℃ for 36 hours by using liquid nitrogen/ethanol as a freeze-drying system to obtain the citric acid modified sisal fiber cross-linked chitosan porous microspheres;
mixing: adding salicylic acid and polyglutamic acid into the citric acid modified sisal fiber cross-linked chitosan porous microspheres, fully mixing, adding starch xanthate and amino trimethylene phosphonic acid, and fully mixing to obtain the sewage treatment agent.
Example 4:
a sewage treatment agent comprises the following raw materials in parts by weight: 9 parts of tartaric acid, 28 parts of modified sisal fiber porous microspheres, 9 parts of polyglycine, 9 parts of starch xanthate and 4 parts of amino trimethylene phosphonic acid; the modified sisal fiber porous microspheres are citric acid modified sisal fiber crosslinked chitosan porous microspheres obtained by carrying out citric acid modification, N-hydroxysuccinimide activation and chitosan crosslinking on sisal fibers.
A preparation method of a sewage treatment agent comprises the following steps:
preparing modified sisal fiber porous microspheres:
dissolving sisal fibers in citric acid, adding sodium hypophosphite, performing hydrothermal reaction in an autoclave at the hydrothermal reaction temperature of 135 ℃ for 5.5 hours, centrifuging after the reaction is finished, taking the lower layer of precipitate, washing and drying to obtain citric acid modified sisal fibers, wherein the molar ratio of the sisal fibers to the citric acid to the sodium hypophosphite is 1:7: 0.15;
dissolving the citric acid modified sisal fibers in water, and then adding N-hydroxysuccinimide for activation for 14min to obtain an activated citric acid modified sisal fiber aqueous solution;
adding the activated citric acid modified sisal fiber aqueous solution into a chitosan aqueous solution, wherein the mass ratio of the activated citric acid modified sisal fibers to the chitosan is 1:4, uniformly stirring, standing and aging to obtain citric acid modified sisal fiber crosslinked chitosan hydrogel;
freeze-drying the citric acid modified sisal fiber cross-linked chitosan hydrogel at-90 ℃ for 42 hours by using liquid nitrogen/ethanol as a freeze-drying system to obtain the citric acid modified sisal fiber cross-linked chitosan porous microspheres;
mixing: and adding tartaric acid and polyglycine into the citric acid modified sisal fiber cross-linked chitosan porous microspheres, fully mixing uniformly, adding starch xanthate and amino trimethylene phosphonic acid, and fully mixing uniformly again to obtain the sewage treatment agent.
Example 5:
a sewage treatment agent comprises the following raw materials in parts by weight: 5-10 parts of lactic acid, 20-30 parts of modified sisal fiber porous microspheres, 5-10 parts of polyasparagine, 5-10 parts of starch xanthate and 1-5 parts of amino trimethylene phosphonic acid; the modified sisal fiber porous microspheres are citric acid modified sisal fiber crosslinked chitosan porous microspheres obtained by carrying out citric acid modification, 1- (3-dimethylaminopropyl) -3-ethylcarbodiimide hydrochloride activation and chitosan crosslinking on sisal fibers.
A preparation method of a sewage treatment agent comprises the following steps:
preparing modified sisal fiber porous microspheres:
dissolving sisal fibers in citric acid, adding sodium hypophosphite, performing hydrothermal reaction in an autoclave at the hydrothermal reaction temperature of 140 ℃ for 6 hours, centrifuging after the reaction is finished, taking the lower layer of precipitate, washing and drying to obtain citric acid modified sisal fibers, wherein the molar ratio of the sisal fibers to the citric acid to the sodium hypophosphite is 1:8: 0.2;
dissolving the citric acid modified sisal fibers in water, and then adding 1- (3-dimethylaminopropyl) -3-ethylcarbodiimide hydrochloride for activation for 15min to obtain an activated citric acid modified sisal fiber aqueous solution;
adding the activated citric acid modified sisal fiber aqueous solution into a chitosan aqueous solution, wherein the mass ratio of the activated citric acid modified sisal fibers to the chitosan is 1:5, uniformly stirring, standing and aging to obtain citric acid modified sisal fiber crosslinked chitosan hydrogel;
freeze-drying the citric acid modified sisal fiber cross-linked chitosan hydrogel at-100 ℃ for 48 hours by using liquid nitrogen/ethanol as a freeze-drying system to obtain the citric acid modified sisal fiber cross-linked chitosan porous microspheres;
mixing: adding lactic acid and polyasparagine into the citric acid modified sisal fiber cross-linked chitosan porous microspheres, fully mixing uniformly, adding starch xanthate and amino trimethylene phosphonic acid, and fully mixing uniformly again to obtain the sewage treatment agent.
Test example:
the sewage treatment agents prepared in examples 1 to 5 and comparative example 1 were used for heavy metal wastewater treatment, and the treatment effects are shown in table 1, unit: mg/L.
TABLE 1
Figure BDA0002513051850000131
As can be seen from Table 1, the sewage treatment agents prepared in examples 1 to 5 of the present invention contained cadmium (Cd) in heavy metal sewage2+) Lead (Pb)2+) Copper (Cu)2+) Nickel (Ni)2+) Zinc (Zn), zinc (Zn)2+) The removal rates are respectively more than 99.9%, more than 99.4%, more than 99.3%, more than 99.8% and more than 99.3%, the removal rates of chromium, manganese and mercury in heavy metal sewage are respectively more than 99.7%, more than 99.9% and more than 99.9%, and the treatment effect is good.
It will be evident to those skilled in the art that the invention is not limited to the details of the foregoing illustrative embodiments, and that the present invention may be embodied in other specific forms without departing from the spirit or essential attributes thereof. The present embodiments are therefore to be considered in all respects as illustrative and not restrictive, the scope of the invention being indicated by the appended claims rather than by the foregoing description, and all changes which come within the meaning and range of equivalency of the claims are therefore intended to be embraced therein. Any reference sign in a claim should not be construed as limiting the claim concerned.

Claims (10)

1. A sewage treatment agent is characterized in that: the composite material comprises the following raw materials in parts by weight: 5-10 parts of organic carboxylic acid, 20-30 parts of modified sisal fiber porous microspheres, 5-10 parts of polyamino acid, 5-10 parts of starch xanthate and 1-5 parts of amino trimethylene phosphonic acid.
2. A wastewater treatment agent according to claim 1, wherein: the modified sisal fiber porous microspheres are citric acid modified sisal fiber crosslinked chitosan porous microspheres obtained by carrying out citric acid modification, activating agent activation and chitosan crosslinking on sisal fibers.
3. A wastewater treatment agent according to claim 1, wherein: the organic carboxylic acid is one or more of lactic acid, hydroxybutyric acid, salicylic acid and tartaric acid.
4. A wastewater treatment agent according to claim 1, wherein: the polyamino acid is polyglycine, polyasparagine or polyglutamic acid.
5. A preparation method of a sewage treatment agent is characterized by comprising the following steps:
preparing modified sisal fiber porous microspheres:
dissolving sisal fibers in citric acid, adding a catalyst, carrying out hydrothermal reaction in a high-pressure kettle, centrifuging after the reaction is finished, taking a lower-layer precipitate, washing and drying to obtain citric acid modified sisal fibers;
dissolving the citric acid modified sisal fibers in water, and then adding an activating agent for activation to obtain an activated citric acid modified sisal fiber aqueous solution;
adding the activated citric acid modified sisal fiber aqueous solution into a chitosan aqueous solution, uniformly stirring, standing and aging to obtain citric acid modified sisal fiber crosslinked chitosan hydrogel;
freeze-drying the citric acid modified sisal fiber cross-linked chitosan hydrogel to obtain citric acid modified sisal fiber cross-linked chitosan porous microspheres;
mixing: and adding organic carboxylic acid and polyamino acid into the citric acid modified sisal fiber crosslinked chitosan porous microspheres, fully mixing uniformly, adding starch xanthate and amino trimethylene phosphonic acid, and fully mixing uniformly again to obtain the sewage treatment agent.
6. The method for preparing a sewage treatment agent according to claim 5, wherein: the mole ratio of the sisal fibers to the citric acid to the catalyst is 1: 4-8: 0.01-0.2; the catalyst is sodium hypophosphite.
7. The method for preparing a sewage treatment agent according to claim 5, wherein: the hydrothermal reaction temperature of the high-pressure kettle is 100-140 ℃, and the reaction time is 4-6 h.
8. The method for preparing a sewage treatment agent according to claim 5, wherein: the activating agent is 1- (3-dimethylaminopropyl) -3-ethylcarbodiimide hydrochloride or N-hydroxysuccinimide; the activation time is 10-15 min.
9. The method for preparing a sewage treatment agent according to claim 5, wherein: the mass ratio of the activated citric acid modified sisal fibers to the chitosan is 1: 2-5.
10. The method for preparing a sewage treatment agent according to claim 5, wherein: the freeze drying system is liquid nitrogen/ethanol, the temperature is-60 to-100 ℃, and the time is 24 to 48 hours.
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Application publication date: 20200922