CN111250053A - Preparation method of water treatment agent for removing heavy metal ions - Google Patents

Preparation method of water treatment agent for removing heavy metal ions Download PDF

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Publication number
CN111250053A
CN111250053A CN202010066646.5A CN202010066646A CN111250053A CN 111250053 A CN111250053 A CN 111250053A CN 202010066646 A CN202010066646 A CN 202010066646A CN 111250053 A CN111250053 A CN 111250053A
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heavy metal
treatment agent
water
water treatment
hours
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CN202010066646.5A
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骆培成
王恒锋
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Southeast University
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Southeast University
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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
    • B01J20/22Solid 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
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/04Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising compounds of alkali metals, alkaline earth metals or magnesium
    • B01J20/048Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising compounds of alkali metals, alkaline earth metals or magnesium containing phosphorus, e.g. phosphates, apatites, hydroxyapatites
    • 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
    • C02F1/286Treatment 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
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/288Treatment of water, waste water, or sewage by sorption using composite sorbents, e.g. coated, impregnated, multi-layered
    • 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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  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Analytical Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Inorganic Chemistry (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

The invention discloses a preparation method of a water treatment agent for removing heavy metal ions, which is prepared by treating animal bones and modifying the animal bones by using cellulose. Uniformly mixing microcrystalline cellulose and bone charcoal materials, adding tap water or deionized water, heating to 70-90 ℃ under continuous stirring, keeping for 2-5 hours, cooling to room temperature, aging for more than 12 hours, filtering and retaining a filter cake material; and (3) washing the filter cake material by using an acidic buffer solution and tap water or deionized water, placing the filter cake material in an oven, and drying at the temperature of 60-120 ℃ for more than 12 hours to obtain the heavy metal ion water treatment agent. The heavy metal ion water treatment agent prepared by the invention has a good removal effect on sewage containing heavy metal ions, and the materials used by the water treatment agent are kitchen garbage animal bones for waste recycling, so that the pollution of raw materials to the environment is reduced, the cost is low, and the water treatment agent has a good application value in the field of treating industrial heavy metal sewage.

Description

Preparation method of water treatment agent for removing heavy metal ions
Technical Field
The invention relates to the field of water treatment, in particular to a water treatment agent for removing heavy metal ions in water and a preparation method thereof.
Background
Due to the discharge of industrial sewage, the problem of heavy metal pollution (including lead, cadmium, copper, nickel and the like) of water bodies is increasingly serious. Heavy metal pollution is different from organic matter pollution, and has the characteristics of stability, difficult degradation, enrichment in organisms through a food chain and even conversion into metal organic matters with higher toxicity, once untreated industrial water is discharged into nature, serious pollution to a water environment can be caused, and the survival of aquatic organisms and the health of human beings can be greatly threatened.
The treatment technology of heavy metal ions mainly adopts a physical chemical method, a chemical method and a biological method, and comprises an ion exchange method, a membrane separation method, an extraction method, an electrolysis method, a biological adsorption method and the like, and the treatment technologies have the advantages of high cost, low removal efficiency and easy occurrence of secondary pollution. The adsorption material prepared by treating and modifying animal bones can fix heavy metal ions, has better adsorption efficiency, can be recycled and has no secondary pollution. Therefore, the adsorption method has better application prospect for heavy metal treatment.
The hydroxyapatite is used as an adsorption material, widely exists in animal bones, not only has higher adsorption capacity and ion exchange capacity, but also has no toxicity and good biocompatibility. Because the surface of the metal ion exchange membrane has metal cations and hydroxyl groups, the metal ion exchange membrane has good exchange and complexation effects on heavy metal cations and organic macromolecules. By compounding organic macromolecules with the same adsorption effect, the metal ion adsorption capacity can be remarkably improved, and the method has active research in the fields of wastewater treatment, soil remediation and the like and shows good application prospects.
Cellulose is a macromolecular polysaccharide composed of glucose and widely exists in plants. It is composed of a large amount of hydroxyl groups, and has a good removal effect on heavy metal ion adsorption. The heavy metal ions are immobilized in the cellulose macromolecules by complexing the metal ions with hydroxyl groups to form metal ion complexes. A large number of studies show that the efficiency of removing heavy metal ions by using modified cellulose is high. Therefore, the absorption efficiency of the cellulose and the treated animal bone can be obviously improved by compounding the cellulose and the treated animal bone.
Disclosure of Invention
The technical problem is as follows: the invention aims to provide a more efficient and more environment-friendly water treatment agent for removing heavy metal ions in water and a preparation method thereof.
The technical scheme is as follows: the preparation method of the water treatment agent for removing heavy metal ions is realized by the following technical scheme:
the method is used for preparing the water treatment adsorbent for removing heavy metal ions in water by treating animal bones and performing surface modification by using microcrystalline cellulose, and comprises the following specific steps:
step 1, immersing animal bones in an alkaline aqueous solution, heating to boil, keeping boiling for 0.5-2 hours, cooling and filtering to obtain treated animal bones, crushing the treated animal bones by a crusher, and sieving the crushed animal bones by a 50-100-mesh sieve to obtain a bone powder material;
step 2, placing the bone powder material in a muffle furnace, heating to 500-800 ℃, keeping for 30 minutes, and cooling to room temperature;
step 3, cleaning the bone powder material subjected to high-temperature treatment for 2-5 times by using tap water or deionized water, and drying for more than 12 hours in an oven at the temperature of 60-80 ℃ to obtain an animal bone charcoal material;
step 4, uniformly mixing the microcrystalline cellulose and the bone charcoal material, adding tap water or deionized water, heating to 70-90 ℃ under continuous stirring, keeping for 2-5 hours, cooling to room temperature, aging for more than 12 hours, filtering and retaining a filter cake material;
and 5, washing the filter cake material by using an acidic buffer solution and tap water or deionized water, placing the filter cake material in an oven, and drying at 60-120 ℃ for more than 12 hours to obtain the heavy metal ion water treatment agent.
Wherein the content of the first and second substances,
and when the material is calcined in a muffle furnace, the required gas atmosphere is nitrogen, and the heating rate and the cooling rate are both 10-40 ℃/min.
In the step 4, the mass ratio of the microcrystalline cellulose to the bone charcoal material is as follows: 1 part of cellulose, 1-5 parts of bone charcoal and 10-50 parts of deionized water or tap water.
In step 5, the pH value range of the acidic buffer solution is between 2 and 6;
and 5, washing by using tap water or deionized water, wherein the pH value of the washing liquid is not more than 8 after the washing reaches the end point.
In step 1, the pH of the aqueous alkaline solution is not less than 12.
Has the advantages that: in conclusion, the method for preparing the water treatment agent for removing the heavy metal ions in the water by adopting the technical scheme of the invention has the advantages of low raw material price, environmental protection, simple operation process, safety and no pollution, the prepared water treatment agent has comprehensive treatment effect when being used for adsorbing the heavy metal ions in the water body, physical adsorption and chemical adsorption are combined, and the heavy metal ions in the wastewater are more comprehensively and thoroughly removed by ion exchange, complexation and physical adsorption, so that the water treatment requirement is met.
Detailed Description
The process according to the invention is better illustrated by the following examples, without the invention being restricted thereby.
Example 1
Taking waste pig bones in kitchen waste, immersing the waste pig bones in 1 mol/L sodium hydroxide aqueous solution, heating the waste pig bones to boil, keeping the waste pig bones to boil for 0.5 hour, filtering the waste pig bones after the boiling for later use;
pulverizing the treated bone with a pulverizer, and sieving with a 50-mesh sieve for later use;
putting the powder into a muffle furnace, heating and pyrolyzing the powder in the nitrogen atmosphere to 500 ℃ and keeping the temperature for 30 minutes, cooling the powder to room temperature, keeping the heating and cooling rate at 20 ℃/minute, and taking the powder out for later use;
washing the pyrolyzed powder with deionized water for 3 times, placing the powder in an oven to dry for 24 hours at 90 ℃, and taking out the powder to obtain bone charcoal for later use;
weighing 1 part of microcrystalline cellulose and 5 parts of bone charcoal according to the mass ratio, uniformly mixing, adding 20 parts of deionized water, heating to 80 ℃ under continuous stirring, keeping for 4 hours, cooling to room temperature, aging for 24 hours, and filtering to obtain required powder precipitate;
washing with citric acid buffer solution and deionized water, and drying in an oven at 60 ℃ for 24 hours to obtain the heavy metal ion water treatment agent.
Example 2:
taking waste ox bones in kitchen waste, immersing the ox bones in 0.01 mol/L sodium hydroxide aqueous solution (pH value is 12), heating the ox bones to boil, keeping the ox bones boiled for 2 hours, filtering the ox bones after the ox bones are boiled, and taking the ox bones out for later use;
pulverizing the treated bone with a pulverizer, and sieving with a 100-mesh sieve for later use;
putting the powder into a muffle furnace, heating and pyrolyzing the powder in the nitrogen atmosphere to reach 800 ℃ and keeping the temperature for 30 minutes, cooling the powder to room temperature, keeping the heating and cooling rate at 40 ℃/minute, and taking the powder out for later use;
washing the pyrolyzed powder with deionized water for 2 times, placing the powder in an oven to dry for 24 hours at 60 ℃, and taking out the powder to obtain bone charcoal for later use;
weighing 1 part of microcrystalline cellulose and 5 parts of bone charcoal according to the mass ratio, uniformly mixing, adding 50 parts of deionized water, heating to 70 ℃ under continuous stirring, keeping for 5 hours, cooling to room temperature, aging for 24 hours, and filtering to obtain required powder precipitate;
washing with citric acid buffer solution and deionized water, and drying in an oven at 60 ℃ for 24 hours to obtain the heavy metal ion water treatment agent.
Example 3:
taking waste pig bones in kitchen waste, immersing the waste pig bones in 0.5 mol/L potassium hydroxide aqueous solution, heating the waste pig bones to boil, keeping the waste pig bones boiled for 1.5 hours, filtering the waste pig bones after the boiling, and taking out the waste pig bones for later use;
pulverizing the treated bone with a pulverizer, and sieving with a 80-mesh sieve for later use;
putting the powder into a muffle furnace, heating and pyrolyzing the powder in the nitrogen atmosphere to 650 ℃, keeping the temperature for 2 hours, cooling the powder to room temperature, keeping the heating and cooling rate at 10 ℃/min, and taking the powder out for later use;
washing the pyrolyzed powder with deionized water for 5 times, placing the powder in an oven to dry for 12 hours at 80 ℃, and taking out the powder to obtain bone charcoal for later use;
weighing 1 part of microcrystalline cellulose and 2 parts of bone charcoal according to the mass ratio, uniformly mixing, adding 25 parts of deionized water, heating to 80 ℃ under continuous stirring, keeping for 3 hours, cooling to room temperature, aging for 24 hours, and filtering to obtain required powder precipitate;
washing with citric acid buffer solution and deionized water, and drying in an oven at 120 ℃ for 12 hours to obtain the heavy metal ion water treatment agent.
Experimental example 1
100mL of a contaminated water sample containing 500ppm of lead ions was added with 500mg of the water treatment agent prepared by the preparation method of example 1, and after stirring for 1.5 hours at 20 ℃ and pH 7, the adsorption was balanced, the lead ion concentration of the treated water sample was reduced from 500ppm to 31.3ppm, the removal rate was 93.7%, and the adsorption capacity was 93.74 mg/g.
Experimental example 2
100mL of a polluted water sample containing 500ppm of cadmium ions is taken, 500mg of the water treatment agent prepared by the preparation method in the embodiment 2 is added, the adsorption is balanced after the polluted water sample is stirred for 2 hours at the temperature of 20 ℃ and under the condition that the pH value is 7, the cadmium ion concentration of the treated water sample is reduced from 500ppm to 42.5ppm, the removal rate reaches 91.5%, and the adsorption capacity is 91.5 mg/g.
Experimental example 3
100ml of an industrial wastewater sample of a certain sewage treatment plant is taken, after the detection of 138ppm of copper ion concentration, 235ppm of lead ion concentration, 86ppm of cadmium ion concentration and 6.2 pH of the water sample, 500mg of the water treatment agent prepared by the preparation method in the embodiment 3 is added, the adsorption is balanced after stirring for 1.5 hours at 20 ℃, the copper ion concentration of the treated water sample is reduced from 138ppm to 2.4ppm, the lead ion concentration is reduced from 235ppm to 0.8ppm, the lead ion concentration is reduced from 86ppm to 1.7ppm, the removal rate of copper ions reaches 98.3%, the removal rate of lead ions reaches 99.7% and the removal rate of cadmium ions reaches 98.0%.

Claims (6)

1. A preparation method of a water treatment agent for removing heavy metal ions is characterized in that after animal bones are treated by the method, microcrystalline cellulose is utilized for surface modification to prepare a water treatment adsorbent for removing the heavy metal ions in water, and the preparation method specifically comprises the following steps:
step 1, immersing animal bones in an alkaline aqueous solution, heating to boil, keeping boiling for 0.5-2 hours, cooling and filtering to obtain treated animal bones, crushing the treated animal bones by a crusher, and sieving the crushed animal bones by a 50-100-mesh sieve to obtain a bone powder material;
step 2, placing the bone powder material in a muffle furnace, heating to 500-800 ℃, keeping for 30 minutes, and cooling to room temperature;
step 3, cleaning the bone powder material subjected to high-temperature treatment for 2-5 times by using tap water or deionized water, and drying for more than 12 hours in an oven at the temperature of 60-80 ℃ to obtain an animal bone charcoal material;
step 4, uniformly mixing the microcrystalline cellulose and the bone charcoal material, adding tap water or deionized water, heating to 70-90 ℃ under continuous stirring, keeping for 2-5 hours, cooling to room temperature, aging for more than 12 hours, and filtering to retain the filter cake material;
and 5, washing the filter cake material by using an acidic buffer solution and tap water or deionized water, placing the filter cake material in an oven, and drying at 60-120 ℃ for more than 12 hours to obtain the heavy metal ion water treatment agent.
2. The preparation method of the water treatment agent for removing the heavy metal ions according to claim 1, wherein in the step 2, a required gas atmosphere is nitrogen gas when the water is calcined in a muffle furnace, and the heating rate and the cooling rate are both 10-40 ℃/min.
3. The preparation method of the water treatment agent for removing heavy metal ions according to claim 1, wherein in the step 4, the mass ratio of the microcrystalline cellulose to the bone char material is as follows: 1 part of cellulose, 1-5 parts of bone charcoal and 10-50 parts of deionized water or tap water.
4. The method for preparing a water treatment agent for removing heavy metal ions according to claim 1, wherein in the step 5, the pH value of the acidic buffer is in the range of 2 to 6.
5. The method according to claim 1, wherein in step 5, the washing is performed with tap water or deionized water, and after the washing reaches an end point, the pH of the washing solution is not greater than 8.
6. The method for producing a water treatment agent for removing heavy metal ions according to claim 1, wherein in the step 1, the pH of the aqueous alkaline solution is not less than 12.
CN202010066646.5A 2020-01-20 2020-01-20 Preparation method of water treatment agent for removing heavy metal ions Pending CN111250053A (en)

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Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105289528A (en) * 2015-12-09 2016-02-03 山东大学(威海) Preparation method of high-efficiency tetraethylenepentamine modified cellulose base heavy metal ion adsorbent
CN106622171A (en) * 2016-12-27 2017-05-10 郑州诚合信息技术有限公司 High-efficient heavy metal capturing agent and preparation method therefor
CN106629973A (en) * 2016-12-18 2017-05-10 钦州市科学技术开发中心 Treating agent for tannery wastewater and preparation method thereof
CN108499544A (en) * 2018-03-27 2018-09-07 广西大学 A kind of preparation method of polystyrene microsphere fiber type element base weight metal absorbent
CN108620032A (en) * 2018-05-18 2018-10-09 云南圣清环保科技有限公司 A kind of heavy metal absorbent and the preparation method and application thereof
CN110510698A (en) * 2019-08-27 2019-11-29 中国科学院合肥物质科学研究院 A method of using biotic environment material pollution control of water object

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105289528A (en) * 2015-12-09 2016-02-03 山东大学(威海) Preparation method of high-efficiency tetraethylenepentamine modified cellulose base heavy metal ion adsorbent
CN106629973A (en) * 2016-12-18 2017-05-10 钦州市科学技术开发中心 Treating agent for tannery wastewater and preparation method thereof
CN106622171A (en) * 2016-12-27 2017-05-10 郑州诚合信息技术有限公司 High-efficient heavy metal capturing agent and preparation method therefor
CN108499544A (en) * 2018-03-27 2018-09-07 广西大学 A kind of preparation method of polystyrene microsphere fiber type element base weight metal absorbent
CN108620032A (en) * 2018-05-18 2018-10-09 云南圣清环保科技有限公司 A kind of heavy metal absorbent and the preparation method and application thereof
CN110510698A (en) * 2019-08-27 2019-11-29 中国科学院合肥物质科学研究院 A method of using biotic environment material pollution control of water object

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
王卫,等: ""鱼骨炭吸附剂吸附重金属研究进展"", 《材料导报》 *

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