CN112169825A - Ion induction catalyst for industrial circulating water treatment and preparation method thereof - Google Patents

Ion induction catalyst for industrial circulating water treatment and preparation method thereof Download PDF

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Publication number
CN112169825A
CN112169825A CN202010994081.7A CN202010994081A CN112169825A CN 112169825 A CN112169825 A CN 112169825A CN 202010994081 A CN202010994081 A CN 202010994081A CN 112169825 A CN112169825 A CN 112169825A
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China
Prior art keywords
circulating water
catalyst
zeolite
ion
vacuum
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CN202010994081.7A
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Chinese (zh)
Inventor
成兰兴
管素敏
赵增兵
刘利民
郭慧君
赵怡丽
徐爱春
杨舒程
罗岗
陈波
张冰
冯胜跃
陈蕾
袁琳
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Henan Haitian Environmental Technology Co ltd
HENAN CHEMICAL INDUSTRY RESEARCH INSTITUTE CO LTD
Henan Academy of Sciences
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Henan Haitian Environmental Technology Co ltd
HENAN CHEMICAL INDUSTRY RESEARCH INSTITUTE CO LTD
Henan Academy of Sciences
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Priority to CN202010994081.7A priority Critical patent/CN112169825A/en
Publication of CN112169825A publication Critical patent/CN112169825A/en
Pending legal-status Critical Current

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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
    • B01J29/00Catalysts comprising molecular sieves
    • B01J35/40
    • B01J35/618
    • 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
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • C02F1/5236Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic 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
    • C02F2101/103Arsenic 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
    • C02F2101/203Iron or iron compound
    • 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

Abstract

An ion-induced catalyst for treating industrial circulating water is prepared from natural zeolite through high-temp pore-forming, vacuum activating in the presence of sodium carbonate solution and sodium hydroxide solution, and drying. The invention has the beneficial effects that: the ion-induced catalyst after pore-forming and activating has greatly increased specific surface area, and makes the adsorption of embedded CO in and on the zeolite pore channel2‑ 3And OHThe method can ensure that the metal ions are rapidly precipitated on the surface of the catalyst and gradually increased to form spherical crystals for discharge, and has good precipitation effect and higher removal rate of the metal ions.

Description

Ion induction catalyst for industrial circulating water treatment and preparation method thereof
Technical Field
The invention relates to the technical field of water treatment, in particular to an ion induction catalyst for industrial circulating water treatment and a preparation method thereof.
Background
In the operation process of large-scale metallurgy, petrochemical industry and chemical industry production, a large amount of industrial circulating water is required to exchange heat generated in the production process so as to ensure productionAnd (5) normally running. A certain amount of Ca exists in the industrial circulating water2+、Mg2+、Fe2+、Mn2+、As3+And F-The plasma can cause great harm such as scaling, corrosion and the like to the equipment pipeline in the operation process, and aims to prevent and reduce Ca in the circulating water2+、Mg2+、Fe2+、Mn2+、As3+And F-The traditional method is to add sufficient antiscale and corrosion inhibitor into the circulating water, the method plays a certain role in antiscale and corrosion inhibition in the using process of the circulating water, but has great defects that firstly, a large amount of medicament needs to be added, which causes waste and increases the operating cost, and on the other hand, because of evaporation loss of water in the operating process of the circulating water, Ca in the circulating water can be caused to be evaporated and lost2+、Mg2+、Fe2+、Mn2+、As3+And F-Plasma constantly enriches, and the concentration increases, needs a large amount of strong brine waste water of discharging and constantly supplyes fresh water and be used for guaranteeing production normal operating, causes the very big waste of water resource, and the emission of strong brine also causes pressure to subsequent high salt waste water treatment simultaneously.
At present, there is also a method of inducing crystallization by adding seed crystal, the seed crystal is added to accelerate the speed of precipitation crystallization and sedimentation, the seed crystal material of the method is usually quartz sand, silicate and the like, but the method only adds seed crystal or adds seed crystal and precipitant, the seed crystal particle is taken as the conventional solid particle, the inducing effect is small, and therefore the speed of inducing crystallization is slow.
Disclosure of Invention
In order to overcome the defects in the prior art, the invention provides the ion-induced catalyst for industrial circulating water treatment and the preparation method thereof, which can quickly crystallize and precipitate metal ions in water, have good precipitation effect and higher removal rate of the metal ions.
An ion-induced catalyst for treating industrial circulating water is prepared from zeolite: sodium carbonate solution: the volume ratio of the sodium hydroxide solution is 1:2-50: 2-50;
the zeolite is natural zeolite with the diameter of 0.1-2.0mm, the mass concentration of a sodium carbonate solution is 10-30%, and the mass concentration of a sodium hydroxide solution is 3-15%.
A preparation method of an ion-induced catalyst for industrial circulating water treatment comprises the following steps:
step one, high-temperature pore forming, namely calcining natural zeolite in a high-temperature furnace, keeping the temperature at 650-850 ℃ for 4-12h, and cooling for later use;
step two, vacuum activation, namely adding calcined natural zeolite into a reaction bottle, vacuumizing the reaction bottle to a limit vacuum state by using a vacuum pump, sucking a sodium carbonate solution and a sodium hydroxide solution in a feeding funnel connected with the reaction bottle into the reaction bottle by using vacuum, opening an emptying valve to release vacuum, soaking for 6-24 hours at normal pressure, and filtering;
and step three, drying, filtering the soaked and activated zeolite, and drying for 4-10 hours at the temperature of 90-110 ℃.
The ratio of the sodium carbonate solution to the sodium hydroxide solution is controlled in a volume ratio of 1: 0.1-1.
The particle diameter D of the ion-induced catalyst50100-2G, density 1-3.5g/cm3
The application and the principle of the invention are as follows:
the ion-induced catalyst is used in an industrial circulating water treatment device to remove Ca in water2+、Mg2+、Fe2+、Mn2+、As3+The ions are concentrated on the catalyst surface where they react with OH added to the system-And CO2Water insoluble precipitate generated by the reaction is attached to the inner hole and the surface of the catalyst and is continuously grown to form spherical particles to be discharged out of the system, thereby removing Ca in the water2+、Mg2+、Fe2 +、Mn2+、As3+The circulating water is purified, the evaporation rate of the circulating water is improved, and the scaling and corrosion hazards of harmful ions in water to the circulating system are reduced. Utilization of purified CO in boiler flue gas2CO as a system3 2-The source, on one hand, saves a large amount of cost, and on the other hand, can greatly reduce the temperatureThe room gas is discharged, and ecological protection and high-quality development are realized.
The ion inducing catalyst for industrial circulating water is prepared with natural zeolite as carrier and through high temperature calcination to modify the inner pore passage of zeolite and raise the specific surface area greatly, and soaking in sodium carbonate and sodium hydroxide solution under vacuum condition to adsorb and inlay CO onto the surface and inner pore passage of zeolite2- 3And OH-. Ca in water2+、Mg2+When the ions enter the interior and the surface of the catalyst to contact with CO2- 3And OH-Combined formation of CaCO3·MgCO3The MgOH precipitates grow inside and on the surface of the support and grow continuously into spherical particles. The spherical particles are dissolved by acid to remove precipitates, and then are activated to be used as the ion-induced catalyst again for recycling.
The invention has the beneficial effects that: the ion induced catalyst after pore forming and activation has greatly increased specific surface area and makes the adsorption of embedded CO in and on the zeolite pore channel2- 3And OH-The method can ensure that the metal ions are rapidly precipitated on the surface of the catalyst and gradually increased to form spherical crystals for discharge, has good precipitation effect and higher removal rate of the metal ions, and can achieve the removal rate of the metal ions reaching over 75 percent when being applied to industrial circulating water treatment; in addition, the ion-induced catalyst provided by the invention has the advantages of low raw material price, simple preparation method and low cost, and can be widely used for softening industrial circulating water in factories.
Detailed Description
Example 1, the present invention provides an ion-induced catalyst for industrial circulating water treatment and a method for preparing the same, which introduces CO using a zeolite porous framework by an impregnation method3 2-And OH-Forming the ion-induced catalyst with the anion-loaded active group.
The ion-induced catalyst is prepared from the following raw materials: sodium carbonate solution: the volume ratio of the sodium hydroxide solution is 1:2: 2; the zeolite is natural zeolite with the diameter of 0.1-2.0mm, the mass concentration of the sodium carbonate solution is 30%, and the mass concentration of the sodium hydroxide solution is 15%.
The preparation method of the ion-induced catalyst comprises the following steps:
step one, high-temperature pore forming, namely calcining 1L of natural zeolite in a high-temperature furnace, keeping the temperature at 650 ℃ for 12 hours, and cooling for later use;
step two, vacuum activation, namely adding calcined natural zeolite into a reaction bottle, vacuumizing the reaction bottle to a limit vacuum state by using a vacuum pump, sucking 2L of sodium carbonate solution (with the mass concentration of 30%) and 2L of sodium hydroxide solution (with the mass concentration of 15%) in a feeding funnel connected with the reaction bottle into the reaction bottle by using vacuum, opening an emptying valve to release vacuum, soaking for 6-24 hours at normal pressure, and filtering;
and step three, drying, filtering the soaked and activated zeolite, and drying for 4 hours at 110 ℃.
Example 2, an ion-inducing catalyst was prepared using the following starting materials, zeolite: sodium carbonate solution: the volume ratio of the sodium hydroxide solution is 1:50: 2; the zeolite is natural zeolite with the diameter of 0.1-2.0mm, the mass concentration of the sodium carbonate solution is 10%, and the mass concentration of the sodium hydroxide solution is 15%.
The preparation method of the ion-induced catalyst comprises the following steps:
step one, high-temperature pore forming, namely calcining 1L of natural zeolite in a high-temperature furnace, keeping the temperature at 850 ℃ for 4 hours, and cooling for later use;
step two, vacuum activation, namely adding calcined natural zeolite into a reaction bottle, vacuumizing the reaction bottle to a limit vacuum state by using a vacuum pump, sucking 50L of sodium carbonate solution (with the mass concentration of 10%) and 2L of sodium hydroxide solution (with the mass concentration of 15%) in a feeding funnel connected with the reaction bottle into the reaction bottle by using vacuum, opening an emptying valve to release vacuum, soaking for 6-24 hours at normal pressure, and filtering;
and step three, drying, filtering the soaked and activated zeolite, and drying at 90 ℃ for 10 h.
Example 3, an ion-inducing catalyst was prepared using the following starting materials, zeolite: sodium carbonate solution: the volume ratio of the sodium hydroxide solution is 1:50: 50; the zeolite is natural zeolite with the diameter of 0.1-2.0mm, the mass concentration of the sodium carbonate solution is 10%, and the mass concentration of the sodium hydroxide solution is 3%.
The preparation method of the ion-induced catalyst comprises the following steps:
step one, high-temperature pore forming, namely calcining 1L of natural zeolite in a high-temperature furnace, keeping the temperature at 700 ℃ for 8 hours, and cooling for later use;
step two, vacuum activation, namely adding calcined natural zeolite into a reaction bottle, vacuumizing the reaction bottle to a limit vacuum state by using a vacuum pump, sucking 50L of sodium carbonate solution (with the mass concentration of 10%) and 50L of sodium hydroxide solution (with the mass concentration of 3%) in a feeding funnel connected with the reaction bottle into the reaction bottle by using vacuum, opening an emptying valve to release vacuum, soaking for 6-24 hours at normal pressure, and filtering;
and step three, drying, filtering the soaked and activated zeolite, and drying for 7 hours at 100 ℃.

Claims (3)

1. An ion induction catalyst for industrial circulating water treatment is characterized by being prepared from the following raw materials: sodium carbonate solution: the volume ratio of the sodium hydroxide solution is 1:2-50: 2-50;
the zeolite is natural zeolite with the diameter of 0.1-2.0mm, the mass concentration of a sodium carbonate solution is 10-30%, and the mass concentration of a sodium hydroxide solution is 3-15%.
2. A preparation method of an ion induction catalyst for industrial circulating water treatment is characterized by comprising the following steps:
step one, high-temperature pore forming, namely calcining natural zeolite in a high-temperature furnace, keeping the temperature at 650-850 ℃ for 4-12h, and cooling for later use;
step two, vacuum activation, namely adding calcined natural zeolite into a reaction bottle, vacuumizing the reaction bottle to a limit vacuum state by using a vacuum pump, sucking a sodium carbonate solution and a sodium hydroxide solution in a feeding funnel connected with the reaction bottle into the reaction bottle by using vacuum, opening an emptying valve to release vacuum, soaking for 6-24 hours at normal pressure, and filtering;
and step three, drying, filtering the soaked and activated zeolite, and drying for 4-10 hours at the temperature of 90-110 ℃.
3. The method for preparing the ion-induced catalyst for industrial circulating water treatment according to claim 2, wherein the ratio of the sodium carbonate solution to the sodium hydroxide solution is controlled in a volume ratio of 1: 0.1-1.
CN202010994081.7A 2020-09-21 2020-09-21 Ion induction catalyst for industrial circulating water treatment and preparation method thereof Pending CN112169825A (en)

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114713185A (en) * 2022-04-22 2022-07-08 重庆三峡学院 Preparation method and application of spherical lanthanum carbonate loaded zeolite phosphate adsorbent

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US20020074293A1 (en) * 2000-12-14 2002-06-20 Kuznicki Steven M. Porous static water softener containing hybrid zeolite-silicate composition
US20020074291A1 (en) * 2000-12-14 2002-06-20 Kuznicki Steven M. Method of static water softening using zeolites of novel morphology
CN201971689U (en) * 2011-01-18 2011-09-14 清华大学 Device for removing and recovering heavy metal by crystallization
CN103373786A (en) * 2012-04-28 2013-10-30 北京林业大学 Method for treating reverse osmosis concentrate
CN106044997A (en) * 2016-07-08 2016-10-26 哈尔滨工业大学深圳研究生院 Treatment method of heavy metal wastewater containing Fe<3+>
CN108383206A (en) * 2018-04-03 2018-08-10 浙江金通科技有限公司 A kind of complexing agent removing fluorine ion in water removal
CN108675466A (en) * 2018-04-23 2018-10-19 天津大学 A kind of preprocess method preventing fouling membrane in coal chemical industry recirculated water reuse
CN108862455A (en) * 2018-07-06 2018-11-23 四川盈乾建设工程有限公司 A kind of river wastewater inorganic agent
CN110193360A (en) * 2019-06-28 2019-09-03 厦门德露滋环保科技有限公司 A kind of induction crystallisation material for water treatment and preparation method thereof
CN110550748A (en) * 2019-09-19 2019-12-10 长沙理工大学 Method and device for removing hardness in water

Patent Citations (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20020074293A1 (en) * 2000-12-14 2002-06-20 Kuznicki Steven M. Porous static water softener containing hybrid zeolite-silicate composition
US20020074291A1 (en) * 2000-12-14 2002-06-20 Kuznicki Steven M. Method of static water softening using zeolites of novel morphology
CN201971689U (en) * 2011-01-18 2011-09-14 清华大学 Device for removing and recovering heavy metal by crystallization
CN103373786A (en) * 2012-04-28 2013-10-30 北京林业大学 Method for treating reverse osmosis concentrate
CN106044997A (en) * 2016-07-08 2016-10-26 哈尔滨工业大学深圳研究生院 Treatment method of heavy metal wastewater containing Fe<3+>
CN108383206A (en) * 2018-04-03 2018-08-10 浙江金通科技有限公司 A kind of complexing agent removing fluorine ion in water removal
CN108675466A (en) * 2018-04-23 2018-10-19 天津大学 A kind of preprocess method preventing fouling membrane in coal chemical industry recirculated water reuse
CN108862455A (en) * 2018-07-06 2018-11-23 四川盈乾建设工程有限公司 A kind of river wastewater inorganic agent
CN110193360A (en) * 2019-06-28 2019-09-03 厦门德露滋环保科技有限公司 A kind of induction crystallisation material for water treatment and preparation method thereof
CN110550748A (en) * 2019-09-19 2019-12-10 长沙理工大学 Method and device for removing hardness in water

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114713185A (en) * 2022-04-22 2022-07-08 重庆三峡学院 Preparation method and application of spherical lanthanum carbonate loaded zeolite phosphate adsorbent

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Inventor after: Cheng Lanxing

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