CN110327904A - A kind of wastewater treatment material and preparation method thereof removing lead waste water - Google Patents

A kind of wastewater treatment material and preparation method thereof removing lead waste water Download PDF

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CN110327904A
CN110327904A CN201910656709.XA CN201910656709A CN110327904A CN 110327904 A CN110327904 A CN 110327904A CN 201910656709 A CN201910656709 A CN 201910656709A CN 110327904 A CN110327904 A CN 110327904A
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waste water
wastewater treatment
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agent
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巫文嵩
曹继仁
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Sichuan Zhengxiang Environmental Protection Technology Co Ltd
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    • 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
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/10Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising silica or silicate
    • B01J20/12Naturally occurring clays or bleaching earth
    • 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
    • B01J20/20Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising free carbon; comprising carbon obtained by carbonising processes
    • 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
    • B01J20/22Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material
    • B01J20/26Synthetic macromolecular compounds
    • B01J20/265Synthetic macromolecular compounds modified or post-treated polymers
    • B01J20/267Cross-linked polymers
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/281Treatment of water, waste water, or sewage by sorption using inorganic sorbents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/283Treatment of water, waste water, or sewage by sorption using coal, charred products, or inorganic mixtures containing them
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/285Treatment of water, waste water, or sewage by sorption using synthetic organic sorbents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/286Treatment of water, waste water, or sewage by sorption using natural organic sorbents or derivatives thereof
    • 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

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Abstract

The invention belongs to lead ion processing technology fields, more particularly to a kind of wastewater treatment material and preparation method thereof for removing lead waste water, the wastewater treatment material are made of raw material from the following weight: 40-50 parts of polyacrylic acid, 10-20 parts of chitosan, 5-10 parts of hemicellulose, 10-15 parts of hydrotalcite, 5-10 parts of graphene, 5-10 parts of ethylenediamine tetra-acetic acid, 5-18 parts of manganese dioxide, 3-8 parts of crosslinking agent, 0.2-0.6 parts of initiator, 0.3-1 parts of coupling agent, 0.5-2 parts of compatilizer, 10-15 parts and dispersing agent 1-2 parts of foaming agent;Wastewater treatment material of the present invention, adsorption capacity is big, can effectively remove the lead ion in waste water, while preparation method is simple.

Description

A kind of wastewater treatment material and preparation method thereof removing lead waste water
Technical field
The invention belongs to lead ion processing technology field more particularly to it is a kind of remove lead waste water wastewater treatment material and Preparation method.
Background technique
With the economic development of country and the support of policy, a large amount of equipment is using battery as driving force, such as lead Sour water battery is applied mostly in tractor, tricycle, automobile start etc., and maintenance-free lead accumulator application range is wider, packet Include uninterruptible power supply, electrical vehicular power, battery of electric bicycle etc..Lead-acid accumulator needs to be divided into constant-current discharge according to application (such as uninterruptible power supply) and spark (such as automobile starting battery).
It is the sorting that needs early period, broken but at present during being recycled lead-acid accumulator, while entering the useless of factory Lead-acid accumulator a part contains sulfuric acid, and sulfur acid, spent acid do not occur mainly with the preprocessing process of waste lead acid battery to a part, The pretreated first step of waste lead acid battery exactly pours out Waste Sulfuric Acid, and focuses on, and to sum up generates during comprehensive utilization A large amount of leaded waste water, as direct emission pollutes environment and damage human health.
Existing lead containing wastewater treatment mainly has: chemical precipitation method, lime stone neutralisation, vulcanization-lime neutralisation-electrolysis Method, membrane separation process, above method handle the ineffective of lead waste water, it is difficult to meet demand.
Summary of the invention
In order to solve the above-mentioned technical problem the present invention provides a kind of wastewater treatment material for removing lead waste water, absorption is held Amount is big, can effectively remove the lead ion in waste water, while preparation method is simple.
The technical scheme to solve the above technical problems is that a kind of wastewater treatment material for removing lead waste water, It is made of raw material from the following weight: 40-50 parts of polyacrylic acid, 10-20 parts of chitosan, 5-10 parts of hemicellulose, hydrotalcite 10- 15 parts, 5-10 parts of graphene, 5-10 parts of ethylenediamine tetra-acetic acid, 5-18 parts of manganese dioxide, 3-8 parts of crosslinking agent, initiator 0.2-0.6 Part, 0.3-1 parts of coupling agent, 0.5-2 parts of compatilizer, 10-15 parts and dispersing agent 1-2 parts of foaming agent.
Based on the above technical solution, the present invention can also be improved as follows.
Further preferably as the present invention, the crosslinking agent is dihydroxymethyl dihydroxy ethyl urea, glutaraldehyde, boric acid, epoxy Chloropropane and N, N, the mixture of one or more of-methylene acrylamide.
Further preferably as the present invention, the initiator is ferrous sulfate, benzoyl peroxide, potassium peroxydisulfate and azo The mixture of one or more of two isobutyl cyanogen.
Further preferably as the present invention, the coupling agent is gamma-aminopropyl-triethoxy-silane or 3- glycidol ether Oxygen propyl trimethoxy silicane.
Further preferably as the present invention, the compatilizer is maleic anhydride graft phenylethene or maleic anhydride grafted propylene Nitrile-butadienestyrene copolymer.
Further preferably the foaming agent is azodicarbonamide, 4 as of the invention, 4 '-oxobenzenesulfonyl hydrazide, right The mixture of one or more of toluene sulfonyl hydrazide, 4,4 '-disulfonyl hydrazides and dinitrosopentamethylene tetramine.
Further preferably as the present invention, the dispersing agent is oxidized polyethylene wax or chlorinated polypropylene wax.
The present invention also provides a kind of preparation methods of wastewater treatment material for removing lead waste water, comprising the following steps:
A, in parts by weight, under the conditions of nitrogen protection, by 40-50 parts of polyacrylic acid, 10-20 parts of chitosan, hemicellulose 5-10 parts plain, 5-10 parts and water 400-500 parts water of ethylenediamine tetra-acetic acid mixes, and obtains mixture, spare;
B, it in parts by weight, is placed in ultrasonic vibration in acid solution by 10-15 parts of hydrotalcite, is then rinsed with water to neutrality, and In 600-800 DEG C of calcining 3-4h, then hydrotalcite is placed in 10-15 parts of the foaming agent mixtures with 100-200 parts of water, finally Under the conditions of 300-400 DEG C of temperature, 1-2h is kept the temperature, pretreated water talcum is obtained;
C, the pretreated water talcum that in parts by weight, step B is obtained is mixed with dispersing agent 1-2 parts, 5-18 parts of manganese dioxide Even carry out ultrasonic disperse, takes out, and be added in reactor after dispersion, then into reactor be added step A obtain mixture with And 0.3-1 parts and compatilizer 0.5-2 parts 5-10 parts of graphene, 3-8 parts of crosslinking agent, 0.2-0.6 parts of initiator, coupling agent mixings, Under the conditions of 80-100 DEG C, it is stirred to react 0.8-1.5h, obtains pretreated waste water processing material;
D, the pretreated waste water processing material that step C is obtained is entered into closed reactor, temperature is controlled in 200-300 DEG C, pressure controls under the conditions of 5-10MPa, and moment release cools down after 8-15min, and repetitive operation three times, is finally obtained for going Except the wastewater treatment material of lead waste water.
The beneficial effects of the present invention are: the present invention utilizes polyacrylic acid, chitosan, hemicellulose and ethylenediamine tetra-acetic acid shape At the skeleton of gel structure, while graphene has strong adsorption capacity and adsorption capacity and high intensity, can effectively improve skeleton Structural strength and adsorpting lead ion increase skeleton surface area by extruding, form Multi net voting cellular structure, have high inhale Attached capacity, furthermore by modified hydrotalcite, increase the interlamellar spacing of hydrotalcite, improve adsorption capacity, manganese dioxide is placed in neatly In the space of rock layers spacing, lead ion is set effectively to be attached to hydrotalcite layers away from space, ethylenediamine tetra-acetic acid and titanium dioxide Manganese has reduction chelation to lead ion, so that lead ion is recycled better effect.
Specific embodiment
The principles and features of the present invention are described below, and the given examples are served only to explain the present invention, is not intended to limit Determine the scope of the present invention.
Embodiment 1
A, under the conditions of nitrogen protection, by polyacrylic acid 40g, chitosan 10g, hemicellulose 5g, ethylenediamine tetra-acetic acid 5g It is mixed with water 400g water, obtains mixture, it is spare;
B, hydrotalcite 10g is placed in ultrasonic vibration in acid solution, be then rinsed with water to neutrality, and in 600 DEG C of calcining 3h, connect Hydrotalcite is placed in the mixture of foaming agent 10g and water 100g, finally under the conditions of 300 DEG C of temperature, keep the temperature 1h, obtain pre- Handle hydrotalcite;
C, the pretreated water talcum for obtaining step B and dispersing agent 1g, manganese dioxide 5g, which are mixed, carries out ultrasonic disperse, dispersion After take out, and be added in reactor, be then added into reactor step A obtain mixture and graphene 5g, crosslinking agent 3g, Initiator 0.2g, coupling agent 0.3g and compatilizer 0.5g are mixed, and under the conditions of 80 DEG C, are stirred to react 0.8h, and it is useless to obtain pretreatment Material for water treatment;
D, the pretreated waste water processing material that step C is obtained is entered into closed reactor, temperature is controlled at 200 DEG C, pressure Under the conditions of 5MPa, moment release cools down after 8min for strong control, and repetitive operation three times, is finally obtained for removing lead waste water Wastewater treatment material.
The crosslinking agent is dihydroxymethyl dihydroxy ethyl urea, and the initiator is ferrous sulfate, and the coupling agent is γ-ammonia Propyl-triethoxysilicane, the compatilizer are maleic anhydride graft phenylethene, and the foaming agent is azodicarbonamide, described Dispersing agent is oxidized polyethylene wax.
Embodiment 2
A, under the conditions of nitrogen protection, by polyacrylic acid 42g, chitosan 12g, hemicellulose 6g, ethylenediamine tetra-acetic acid 6g It is mixed with water 420g water, obtains mixture, it is spare;
B, hydrotalcite 11g is placed in ultrasonic vibration in acid solution, is then rinsed with water to neutrality, and in 620 DEG C of calcining 3.2h, Then hydrotalcite is placed in the mixture of foaming agent 11g and water 120g, finally under the conditions of 320 DEG C of temperature, keeps the temperature 1.2h, obtain To pretreated water talcum;
C, the pretreated water talcum for obtaining step B and dispersing agent 1.2g, manganese dioxide 6g, which are mixed, carries out ultrasonic disperse, point It takes out, and is added in reactor after dissipating, step A is then added into reactor and obtains mixture and graphene 6g, crosslinking agent 4g, initiator 0.3g, coupling agent 0.4g and compatilizer 0.6g are mixed, and under the conditions of 85 DEG C, are stirred to react 0.9h, are pre-processed Wastewater treatment material;
D, the pretreated waste water processing material that step C is obtained is entered into closed reactor, temperature is controlled at 220 DEG C, pressure Under the conditions of 6MPa, moment release cools down after 9min for strong control, and repetitive operation three times, is finally obtained for removing lead waste water Wastewater treatment material.
The crosslinking agent is glutaraldehyde, and the initiator is benzoyl peroxide, and the coupling agent is 3- glycidol ether Oxygen propyl trimethoxy silicane, the compatilizer are maleic anhydride grafted propylene nitrile-butadienestyrene copolymer, the foaming Agent is 4,4 '-oxobenzenesulfonyl hydrazide, and the dispersing agent is chlorinated polypropylene wax.
Embodiment 3
A, under the conditions of nitrogen protection, by polyacrylic acid 44g, chitosan 14g, hemicellulose 7g, ethylenediamine tetra-acetic acid 7g It is mixed with water 440g water, obtains mixture, it is spare;
B, hydrotalcite 12g is placed in ultrasonic vibration in acid solution, is then rinsed with water to neutrality, and in 640 DEG C of calcining 3.4h, Then hydrotalcite is placed in the mixture of foaming agent 12g and water 160g, finally under the conditions of 360 DEG C of temperature, keeps the temperature 1.4h, obtain To pretreated water talcum;
C, the pretreated water talcum for obtaining step B and dispersing agent 1.4g, manganese dioxide 7g, which are mixed, carries out ultrasonic disperse, point It takes out, and is added in reactor after dissipating, step A is then added into reactor and obtains mixture and graphene 7g, crosslinking agent 5g, initiator 0.4g, coupling agent 0.5g and compatilizer 0.8g are mixed, and under the conditions of 85 DEG C, are stirred to react 1h, and it is useless to obtain pretreatment Material for water treatment;
D, the pretreated waste water processing material that step C is obtained is entered into closed reactor, temperature is controlled at 240 DEG C, pressure Under the conditions of 7MPa, moment release cools down after 10min for strong control, and repetitive operation three times, is finally obtained for removing lead waste water Wastewater treatment material.
The crosslinking agent is boric acid, and the initiator is potassium peroxydisulfate, and the coupling agent is 3- glycidyl ether oxygen propyl Trimethoxy silane, the compatilizer are maleic anhydride grafted propylene nitrile-butadienestyrene copolymer, and the foaming agent is pair Toluene sulfonyl hydrazide, the dispersing agent are chlorinated polypropylene wax.
Embodiment 4
A, under the conditions of nitrogen protection, by polyacrylic acid 48g, chitosan 18g, hemicellulose 9g, ethylenediamine tetra-acetic acid 9g It is mixed with water 480g water, obtains mixture, it is spare;
B, hydrotalcite 14g is placed in ultrasonic vibration in acid solution, is then rinsed with water to neutrality, and in 780 DEG C of calcining 3.8h, Then hydrotalcite is placed in the mixture of foaming agent 14g and water 180g, finally under the conditions of 380 DEG C of temperature, keeps the temperature 1.5h, obtain To pretreated water talcum;
C, the pretreated water talcum for obtaining step B and dispersing agent 1.8g, manganese dioxide 15g, which are mixed, carries out ultrasonic disperse, It takes out, and is added in reactor after dispersion, step A is then added into reactor and obtains mixture and graphene 8g, crosslinking Agent 7g, initiator 0.5g, coupling agent 0.8g and compatilizer 1.8g are mixed, and under the conditions of 98 DEG C, are stirred to react 1.3h, are obtained pre- place Manage wastewater treatment material;
D, the pretreated waste water processing material that step C is obtained is entered into closed reactor, temperature is controlled at 280 DEG C, pressure Under the conditions of 8MPa, moment release cools down after 13min for strong control, and repetitive operation three times, is finally obtained for removing lead waste water Wastewater treatment material.
The crosslinking agent is epoxychloropropane, and the initiator is azo-bis-isobutyl cyanide, and the coupling agent is γ-aminopropyl Triethoxysilane, the compatilizer are maleic anhydride grafted propylene nitrile-butadienestyrene copolymer, and the foaming agent is 4, 4 '-disulfonyl hydrazides, the dispersing agent are chlorinated polypropylene wax.
Embodiment 5
A, under the conditions of nitrogen protection, by polyacrylic acid 50g, chitosan 20g, hemicellulose 10g, ethylenediamine tetra-acetic acid 10g and water 500g water mix, and obtain mixture, spare;
B, hydrotalcite 15g is placed in ultrasonic vibration in acid solution, be then rinsed with water to neutrality, and in 800 DEG C of calcining 4h, connect Hydrotalcite is placed in the mixture of foaming agent 15g and water 200g, finally under the conditions of 400 DEG C of temperature, keep the temperature 2h, obtain pre- Handle hydrotalcite;
C, the pretreated water talcum for obtaining step B and dispersing agent 2g, manganese dioxide 18g, which are mixed, carries out ultrasonic disperse, point It takes out, and is added in reactor after dissipating, step A is then added into reactor and obtains mixture and graphene 10g, crosslinking agent 8g, initiator 0.6g, coupling agent 1g and compatilizer 2g are mixed, and under the conditions of 100 DEG C, are stirred to react 1.5h, and it is useless to obtain pretreatment Material for water treatment;
D, the pretreated waste water processing material that step C is obtained is entered into closed reactor, temperature is controlled at 300 DEG C, pressure Under the conditions of 10MPa, moment release cools down after 15min for strong control, and repetitive operation three times, is finally obtained for removing lead waste water Wastewater treatment material.
The crosslinking agent is N, N, and-methylene acrylamide, the initiator is azo-bis-isobutyl cyanide, and the coupling agent is 3- glycidyl ether oxygen propyl trimethoxy silicane, the compatilizer are that maleic anhydride grafted propylene nitrile-butadiene styrene is total Polymers, the foaming agent are dinitrosopentamethylene tetramine, and the dispersing agent is chlorinated polypropylene wax.
Comparative example 1
A, under the conditions of nitrogen protection, by polyacrylic acid 30g, chitosan 5g, hemicellulose 3g, ethylenediamine tetra-acetic acid 3g with Water 200g water mixes, and obtains mixture, spare;
B, hydrotalcite 5g is placed in ultrasonic vibration in acid solution, be then rinsed with water to neutrality, and in 500 DEG C of calcining 1h, connect Hydrotalcite is placed in the mixture of foaming agent 5g and water 50g, finally under the conditions of 200 DEG C of temperature, keep the temperature 0.5h, obtain pre- Handle hydrotalcite;
C, the pretreated water talcum for obtaining step B and dispersing agent 0.5g, manganese dioxide 4g, which are mixed, carries out ultrasonic disperse, point It takes out, and is added in reactor after dissipating, step A is then added into reactor and obtains mixture and graphene 3g, crosslinking agent 1g, initiator 0.1g, coupling agent 0.2g and compatilizer 0.3g are mixed, and under the conditions of 70 DEG C, are stirred to react 0.5h, are pre-processed Wastewater treatment material;
D, the pretreated waste water processing material that step C is obtained is entered into closed reactor, temperature is controlled at 100 DEG C, pressure Under the conditions of 3MPa, moment release cools down after 7min for strong control, and repetitive operation three times, is finally obtained for removing lead waste water Wastewater treatment material.
The crosslinking agent is dihydroxymethyl dihydroxy ethyl urea, and the initiator is ferrous sulfate, and the coupling agent is γ-ammonia Propyl-triethoxysilicane, the compatilizer are maleic anhydride graft phenylethene, and the foaming agent is azodicarbonamide, described Dispersing agent is oxidized polyethylene wax.
Comparative example 2
A, under the conditions of nitrogen protection, by polyacrylic acid 55g, chitosan 25g, hemicellulose 15g, ethylenediamine tetra-acetic acid 15g and water 550g water mix, and obtain mixture, spare;
B, hydrotalcite 20g is placed in ultrasonic vibration in acid solution, be then rinsed with water to neutrality, and in 900 DEG C of calcining 6h, connect Hydrotalcite is placed in the mixture of foaming agent 20g and water 300g, finally under the conditions of 500 DEG C of temperature, keep the temperature 3h, obtain pre- Handle hydrotalcite;
C, the pretreated water talcum for obtaining step B and dispersing agent 3g, manganese dioxide 20g, which are mixed, carries out ultrasonic disperse, point It takes out, and is added in reactor after dissipating, step A is then added into reactor and obtains mixture and graphene 15g, crosslinking agent 10g, initiator 1g, coupling agent 2g and compatilizer 3g are mixed, and under the conditions of 200 DEG C, are stirred to react 2h, are obtained at pretreated waste water Manage material;
D, the pretreated waste water processing material that step C is obtained is entered into closed reactor, temperature is controlled at 400 DEG C, pressure Under the conditions of 15MPa, moment release cools down after 20min for strong control, and repetitive operation three times, is finally obtained for removing lead waste water Wastewater treatment material.
The crosslinking agent is N, N, and-methylene acrylamide, the initiator is azo-bis-isobutyl cyanide, and the coupling agent is 3- glycidyl ether oxygen propyl trimethoxy silicane, the compatilizer are that maleic anhydride grafted propylene nitrile-butadiene styrene is total Polymers, the foaming agent are dinitrosopentamethylene tetramine, and the dispersing agent is chlorinated polypropylene wax.
Embodiment 1-5 and comparative example 1-2 the wastewater treatment material being prepared and existing polyvinyl alcohol gel are inhaled Enclosure material (comparative example 3), being separately added into Pb In Exhausted Water ion concentration is 100mg/L, and temperature is 30 DEG C, pH 7.3, and absorption is held It measures as shown in table 1 below with removal rate:
Table 1
By table 1 it is found that wastewater treatment material of the present invention is big to the adsorption capacity of lead ion, removal efficiency is high.
The foregoing is merely presently preferred embodiments of the present invention, is not intended to limit the invention, it is all in spirit of the invention and Within principle, any modification, equivalent replacement, improvement and so on be should all be included in the protection scope of the present invention.

Claims (8)

1. a kind of wastewater treatment material for removing lead waste water, which is characterized in that be made of raw material from the following weight: polypropylene 40-50 parts sour, 10-20 parts of chitosan, 5-10 parts of hemicellulose, 10-15 parts of hydrotalcite, 5-10 parts of graphene, ethylenediamine tetrem 5-10 parts sour, 5-18 parts of manganese dioxide, 3-8 parts of crosslinking agent, 0.2-0.6 parts of initiator, 0.3-1 parts of coupling agent, compatilizer 0.5-2 10-15 parts and dispersing agent 1-2 parts of part, foaming agent.
2. a kind of wastewater treatment material for removing lead waste water according to claim 1, which is characterized in that the crosslinking agent is Dihydroxymethyl dihydroxy ethyl urea, glutaraldehyde, boric acid, epoxychloropropane and N, N, one or more of-methylene acrylamide Mixture.
3. a kind of wastewater treatment material for removing lead waste water according to claim 1, which is characterized in that the initiator is The mixture of one or more of ferrous sulfate, benzoyl peroxide, potassium peroxydisulfate and azo-bis-isobutyl cyanide.
4. a kind of wastewater treatment material for removing lead waste water according to claim 1, which is characterized in that the coupling agent is Gamma-aminopropyl-triethoxy-silane or 3- glycidyl ether oxygen propyl trimethoxy silicane.
5. a kind of wastewater treatment material for removing lead waste water according to claim 1, which is characterized in that the compatilizer is Maleic anhydride graft phenylethene or maleic anhydride grafted propylene nitrile-butadienestyrene copolymer.
6. a kind of wastewater treatment material for removing lead waste water according to claim 1, which is characterized in that the foaming agent is Azodicarbonamide, 4,4 '-oxobenzenesulfonyl hydrazide, unifor, 4,4 '-disulfonyl hydrazides and dinitroso pentamethylene The mixture of one or more of tetramine.
7. a kind of wastewater treatment material for removing lead waste water according to claim 1, which is characterized in that the dispersing agent is Oxidized polyethylene wax or chlorinated polypropylene wax.
8. a kind of preparation method for the wastewater treatment material for removing lead waste water, which comprises the following steps:
A, in parts by weight, under the conditions of nitrogen protection, by 40-50 parts of polyacrylic acid, 10-20 parts of chitosan, hemicellulose 5- 10 parts, 5-10 parts of ethylenediamine tetra-acetic acid mix with water 400-500 parts of water, obtain mixture, spare;
B, it in parts by weight, is placed in ultrasonic vibration in acid solution by 10-15 parts of hydrotalcite, is then rinsed with water to neutrality, and Hydrotalcite is then placed in 10-15 parts of the foaming agent mixtures with 100-200 parts of water, finally exists by 600-800 DEG C of calcining 3-4h Under the conditions of 300-400 DEG C of temperature, 1-2h is kept the temperature, pretreated water talcum is obtained;
C, in parts by weight, by pretreated water talcum that step B is obtained with dispersing agent 1-2 parts, 5-18 parts of manganese dioxide mix into Row ultrasonic disperse takes out after dispersion, and is added in reactor, and step A is then added into reactor and obtains mixture and stone Black alkene 5-10 parts, 3-8 parts of crosslinking agent, 0.3-1 parts and compatilizer 0.5-2 parts 0.2-0.6 parts of initiator, coupling agent mixings, in 80- Under the conditions of 100 DEG C, it is stirred to react 0.8-1.5h, obtains pretreated waste water processing material;
D, the pretreated waste water processing material that step C is obtained is entered into closed reactor, temperature is controlled at 200-300 DEG C, pressure Under the conditions of 5-10MPa, moment release cools down after 8-15min for strong control, and repetitive operation three times, finally obtains leaded for removing The wastewater treatment material of waste water.
CN201910656709.XA 2019-07-19 2019-07-19 A kind of wastewater treatment material and preparation method thereof removing lead waste water Pending CN110327904A (en)

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Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112191236A (en) * 2020-09-24 2021-01-08 成都玉龙化工有限公司 Adsorbing material and preparation method thereof
CN112209456A (en) * 2020-09-24 2021-01-12 成都玉龙化工有限公司 Water treatment agent and preparation method thereof
CN113509918A (en) * 2020-11-25 2021-10-19 中国科学院青海盐湖研究所 Preparation method of heteropolyacid salt ion sieve adsorbent particles for extracting liquid rubidium and cesium resources
CN115073975A (en) * 2022-06-16 2022-09-20 武汉理工大学 Biodegradable solid lead packaging coating applied to perovskite solar cell and preparation and packaging methods thereof
CN115286063A (en) * 2022-09-09 2022-11-04 湖北众净环保科技有限公司 Sewage treatment agent based on polyaluminium chloride and preparation method thereof
CN116814206A (en) * 2023-06-29 2023-09-29 深圳未来新材料实业有限公司 Epoxy sealant for flexible display screen and preparation method thereof

Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102908985A (en) * 2012-11-12 2013-02-06 湖北中非膨润土有限公司 Bentonite compounded porous material and preparation method thereof
CN202921326U (en) * 2012-11-12 2013-05-08 湖北中非膨润土有限公司 Bentonite composite porous foam plate
CN104741077A (en) * 2013-12-31 2015-07-01 西北大学 Preparation method of carbon adsorption material
CN104941582A (en) * 2015-06-21 2015-09-30 魏健 Negative-ion-containing carbon-based mineral crystal air purification particles and manufacturing method thereof
CN105536734A (en) * 2015-12-25 2016-05-04 成都新柯力化工科技有限公司 Polyvinyl alcohol gel composite material for sewage treatment and preparation method thereof
CN106140114A (en) * 2016-07-28 2016-11-23 陕西科技大学 A kind of adsorbing heavy metal ions composite porous and its preparation method and application
CN106732420A (en) * 2016-12-20 2017-05-31 庆阳敦博科技发展有限公司 A kind of composite for processing heavy metal nickel waste water

Patent Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102908985A (en) * 2012-11-12 2013-02-06 湖北中非膨润土有限公司 Bentonite compounded porous material and preparation method thereof
CN202921326U (en) * 2012-11-12 2013-05-08 湖北中非膨润土有限公司 Bentonite composite porous foam plate
CN104741077A (en) * 2013-12-31 2015-07-01 西北大学 Preparation method of carbon adsorption material
CN104941582A (en) * 2015-06-21 2015-09-30 魏健 Negative-ion-containing carbon-based mineral crystal air purification particles and manufacturing method thereof
CN105536734A (en) * 2015-12-25 2016-05-04 成都新柯力化工科技有限公司 Polyvinyl alcohol gel composite material for sewage treatment and preparation method thereof
CN106140114A (en) * 2016-07-28 2016-11-23 陕西科技大学 A kind of adsorbing heavy metal ions composite porous and its preparation method and application
CN106732420A (en) * 2016-12-20 2017-05-31 庆阳敦博科技发展有限公司 A kind of composite for processing heavy metal nickel waste water

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112191236A (en) * 2020-09-24 2021-01-08 成都玉龙化工有限公司 Adsorbing material and preparation method thereof
CN112209456A (en) * 2020-09-24 2021-01-12 成都玉龙化工有限公司 Water treatment agent and preparation method thereof
CN113509918A (en) * 2020-11-25 2021-10-19 中国科学院青海盐湖研究所 Preparation method of heteropolyacid salt ion sieve adsorbent particles for extracting liquid rubidium and cesium resources
CN115073975A (en) * 2022-06-16 2022-09-20 武汉理工大学 Biodegradable solid lead packaging coating applied to perovskite solar cell and preparation and packaging methods thereof
CN115286063A (en) * 2022-09-09 2022-11-04 湖北众净环保科技有限公司 Sewage treatment agent based on polyaluminium chloride and preparation method thereof
CN115286063B (en) * 2022-09-09 2023-09-22 湖北众净环保科技有限公司 Sewage treatment agent based on polyaluminium chloride and preparation method thereof
CN116814206A (en) * 2023-06-29 2023-09-29 深圳未来新材料实业有限公司 Epoxy sealant for flexible display screen and preparation method thereof
CN116814206B (en) * 2023-06-29 2024-03-01 深圳未来新材料实业有限公司 Epoxy sealant for flexible display screen and preparation method thereof

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