CN104148004A - Magnetic fluorine ion adsorbent and preparation method thereof - Google Patents

Magnetic fluorine ion adsorbent and preparation method thereof Download PDF

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CN104148004A
CN104148004A CN201410436425.7A CN201410436425A CN104148004A CN 104148004 A CN104148004 A CN 104148004A CN 201410436425 A CN201410436425 A CN 201410436425A CN 104148004 A CN104148004 A CN 104148004A
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magnetic
fluorine ion
preparation
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CN104148004B (en
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蒋华麟
陈萍华
厉梦琳
罗胜联
张为波
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Nanchang Hangkong University
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Abstract

The invention discloses a magnetic fluorine ion adsorbent and a preparation method thereof. The magnetic fluorine ion adsorbent comprises the following three components at the same time: Fe3O4, ZrO2-CeO2 composite and La2(C2O4)3. The preparation method comprises the following steps: dispersing nano-sized Fe3O4 of which the surface is modified by SiO2 and an auxiliary agent into deionized water containing ammonia water and ethanol, performing ultrasonic treatment, stirring and uniformly mixing, adding ZrOCl2.8H2O and Ce(NO3)3.6H2O, adding lanthanum nitrate after reaction, uniformly mixing, dripping an oxalic acid solution, and finally, collecting a product by using a magnet and washing and drying the product. The produced adsorbing material is regular in shape, can adsorb a large number of fluoride ions in water, is magnetic, and can perform solid-liquid separation conveniently by virtue of a magnetic force during either preparation of the material or the practical application; the adsorbent has a wide application prospect in an aspect of treating a large volume of high-concentration fluoride-containing wastewater.

Description

A kind of magnetic fluorine ion absorber and preparation method thereof
Technical field
The invention belongs to sorbing material technical field, be specifically related to magnetic fluorine ion absorber of a kind of tool and preparation method thereof.
Background technology
The fluorine disease of drinking high-fluorine water and causing be distribute in the world the most widely endemic disease this.There is underground water fluoride pollution in China, except Shanghai and Hainan, other provinces,municipalities and autonomous regions all have fluorine poisoning in various degree to occur comparatively at large.For the fluorine content in drinking water, have strict demand in the world, in World Health Organization's regulation drinking water, the safe level of fluorine is 0.6-1.5 mg/L, and in China's Drinking Water, the maximum permissible concentration of fluorine is 1 mg/L.Long-term drinking fluorinated volume can cause chronic fluorine poisoning higher than the high-fluorine water of 1.5 mg/L, and tooth, bone, nervous system, digestive system, respiratory system and reproductive system are produced and poisoned.Therefore, develop efficient fluorine removal technology very urgent.
In numerous drinking water defluorination methods, absorption method because it is simple, easy to operate, cost is low is considered to the most promising method.Aspect sorbing material, the fluorine ion absorption property of the materials such as oxide of rare earth and some transition metal obtains extensive concern, and the novel fluorine ion absorber based on this class developing material is just becoming current study hotspot.For example, patent [fluoride ion removing agent and the method for using the sewage that its processing contains fluorine ion, application number 01122878.4] proposed to contain a kind of aqueous hydrochloric acid solution of and calcium carbonate reaction and a kind of rare earth element as the fluoride ion removing agent of the aqueous solution of cerium, lanthanum or its mixture etc., but it also needs to utilize flocculant while using, thereby makes complicated operation; Patent [a kind of composite metal oxide de-fluoridation adsorbent, application number 200510116751.0] a kind of composite metal oxide de-fluoridation adsorbent proposed, it contains transition metal, aluminium and rare earth metal, aluminium is as the most effective one of the composition of this adsorbent, may cause the narrower and easy stripping intoxicating of aluminium of applicable pH range; Patent [attapulgite defluorination agent, 200510040604.x] a kind of adsorbent being comprised of active attapulgite clay, edible alum, calcium oxide, calcium sulfate and sym-closene proposed, although material cost is lower, but adsorbent adsorbance is less, and need the unit such as complicated flocculation, precipitation, clarification filtration to realize Separation of Solid and Liquid, complicated operation.
In addition, at present common fluorine ion absorber the means such as conventionally need be taked to filter, centrifugal and realize Separation of Solid and Liquid, and the recovery of adsorbing saturated adsorbent is wasted time and energy.And adsorbent has been enrichment but not degradation to pollutant, can not be separated from processed liquid up hill and dale fast after saturated if reach absorption, can cause secondary pollution to processed liquid.Magnetic adsorptive material can be promptly under the effect of externally-applied magnetic field by enrichment, thereby obtain effectively separated and reclaim, and easy and simple to handle.Magnetic fluorine ion absorber the present invention relates to and preparation method thereof contains Fe simultaneously 3o 4, ZrO 2-CeO 2compound and La 2(C 2o 4) 3three kinds of components, material has the convenient recovery of magnetic, and adsorbance is up to 125 mg/g, and described material and preparation method thereof has no relevant report.
Summary of the invention
The object of the present invention is to provide a kind of magnetic fluorine ion absorber and preparation method thereof, this civilization is to adopt following means to realize:
(1) with hydro-thermal method to nanometer Fe 3o 4surface is with SiO 2modify the Fe having modified 3o 4, P123 and MgSO 4be dissolved in deionized water, then add 28% concentrated ammonia liquor and ethanol, ultrasonic dispersion, stirs;
(2) by ZrOCl 28H 2o and Ce (NO 3) 36H 2o is added in above-mentioned solution, stirs, and gained solid is separated with magnet, washing, and after refluxing with apparatus,Soxhlet's with acetone, gained solid is Fe 3o 4@ZrO 2-CeO 2, leaned on Magnetic Isolation, washing, dry;
(3) by Fe 3o 4@ZrO 2-CeO 2be placed in beaker, add the lanthanum nitrate of 1 mol/L, mix, stir after a period of time, by oxalic acid wiring solution-forming soluble in water, then oxalic acid solution is slowly added drop-wise in above-mentioned beaker, stir, finally with magnet, collect product, washing, dries.
Magnetic fluorine ion absorber of the present invention, its characteristic component contains Fe simultaneously 3o 4, ZrO 2-CeO 2compound and La 2(C 2o 4) 3three kinds of components.
Preparation Fe of the present invention 3o 4@ZrO 2-CeO 2time, auxiliary material used is surfactant P123 and inorganic salts MgSO 4, and Fe 3o 4: P123:MgSO 4mass ratio be: 1:0.5:0.5 to 1:0.5:2.
Preparation Fe of the present invention 3o 4@ZrO 2-CeO 2time, Fe used 3o 4quality and ZrOCl 28H2O
Add Ce (NO 3) 36H 2the quality of O and ratio be 1:5 to 1:10.
Advantage of the present invention is: prepared fluorine ion sorbing material has efficient Fluoride-Absorption Capacity, maximal absorptive capacity can reach 125mg/g, and, material has magnetic, can utilize easily magnetic force to reclaim adsorbent, no matter this be in the preparation process of material if making, or in the practical application of material, simplify the process of Separation of Solid and Liquid, made material be suitable for applying on a large scale.
Accompanying drawing explanation
Fig. 1 is the scanning electron microscope (SEM) photograph of the present invention's embodiment 1 resulting sorbing material.
Fig. 2 is the adsorption isotherm line chart of the present invention's the resulting sorbing material Adsorption of fluoride of embodiment 1 ion.
Fig. 3 is the time of equilibrium adsorption figure (fluorine ion initial concentration is 300mg/L) of the present invention's the resulting sorbing material Adsorption of fluoride of embodiment 1 ion.
The specific embodiment
Below embodiments of the invention are described in further detail, but the present embodiment is not limited to the present invention, every employing analog structure of the present invention and similar variation thereof, all should list protection scope of the present invention in.
embodiment 1
Utilize conventional hydrothermal method to nanometer Fe 3o 4carry out with SiO 2finishing.Take the nanometer Fe that 0.4g modifies 3o 4, 0.2g P123 and 0.3 g MgSO 4be dissolved in 160 ml deionized waters, then add concentrated ammonia liquor and the 120 ml ethanol of 3 ml 28%, ultrasonic 15 min, stir 45 min.Claim 1.28 g ZrOCl 28H 2o and 1.72 g Ce (NO 3) 36H 2o is added in above-mentioned solution, stirs 8 h.Gained solid is separated with magnet, washing, after using acetone with apparatus,Soxhlet's backflow 48h, gained solid is Fe 3o 4@ZrO 2-CeO 2, leaned on Magnetic Isolation, washing, dry;
Claim 1.2 g Fe 3o 4@ZrO 2-CeO 2in beaker, add 4.43 ml 1mol/L lanthanum nitrates, mix, stir 2 h.Then excessive oxalic acid 1.6748 g are dissolved in to wiring solution-forming in 22 ml water.Again oxalic acid solution is slowly added drop-wise in above-mentioned beaker to approximately 1 h.Stir, approximately 4 h.Finally with magnet, collect product, washing, more than 60 ℃ of oven dry 13 h.
embodiment 2
Utilize conventional hydrothermal method to nanometer Fe 3o 4carry out with SiO 2finishing.Take the nanometer Fe that 0.4g modifies 3o 4, 0.2g P123 and 0.2 g MgSO 4be dissolved in 160 ml deionized waters, then add concentrated ammonia liquor and the 120 ml ethanol of 3 ml 28%, ultrasonic 15 min, stir 45 min.Claim 0.85 g ZrOCl 28H 2o and 1.15 g Ce (NO 3) 36H 2o is added in above-mentioned solution, stirs 8 h.Gained solid is separated with magnet, washing, after using acetone with apparatus,Soxhlet's backflow 48h, gained solid is Fe 3o 4@ZrO 2-CeO 2, leaned on Magnetic Isolation, washing, dry;
Claim 1.2 g Fe 3o 4@ZrO 2-CeO 2in beaker, add 4.43 ml 1mol/L lanthanum nitrates, mix, stir 2 h.Then excessive oxalic acid 1.6748 g are dissolved in to wiring solution-forming in 22 ml water.Again oxalic acid solution is slowly added drop-wise in above-mentioned beaker to approximately 1 h.Stir, approximately 4 h.Finally with magnet, collect product, washing, more than 60 ℃ of oven dry 13 h.
embodiment 3
Utilize conventional hydrothermal method to nanometer Fe 3o 4carry out with SiO 2finishing.Take the nanometer Fe that 0.4g modifies 3o 4, 0.2g P123 and 0.8 g MgSO 4be dissolved in 160 ml deionized waters, then add concentrated ammonia liquor and the 120 ml ethanol of 3 ml 28%, ultrasonic 15 min, stir 45 min.Claim 1.71 g ZrOCl 28H 2o and 2.29 g Ce (NO 3) 36H 2o is added in above-mentioned solution, stirs 8 h.Gained solid is separated with magnet, washing, after using acetone with apparatus,Soxhlet's backflow 48h, gained solid is Fe 3o 4@ZrO 2-CeO 2, leaned on Magnetic Isolation, washing, dry;
Claim 1.2 g Fe 3o 4@ZrO 2-CeO 2in beaker, add 4.43 ml 1mol/L lanthanum nitrates, mix, stir 2 h.Then excessive oxalic acid 1.6748 g are dissolved in to wiring solution-forming in 22 ml water.Again oxalic acid solution is slowly added drop-wise in above-mentioned beaker to approximately 1 h.Stir, approximately 4 h.Finally with magnet, collect product, washing, more than 60 ℃ of oven dry 13 h.
To the maximal absorptive capacity of fluorine ion, (the Langmuir-Freundlich formula of take calculating) is 125 mg/g to the fluorine ion absorber of preparing according to the method, and the time of equilibrium adsorption of the solution that is 300mg/L to fluorine ion initial concentration is about 60 min.Specifically respectively shown in accompanying drawing 2,3.

Claims (5)

1. a magnetic fluorine ion absorber, its characteristic component contains Fe simultaneously 3o 4, ZrO 2-CeO 2compound and La 2(C 2o 4) 3three kinds.
2. a kind of magnetic fluorine ion absorber as claimed in claim 1, is characterized in that described preparation Fe 3o 4@ZrO 2-CeO 2time, auxiliary material used is surfactant P123 and inorganic salts MgSO 4.
3. a kind of magnetic fluorine ion absorber as claimed in claim 2, is characterized in that described Fe 3o 4: P123:MgSO 4mass ratio be: 1:0.5:0.5 to 1:0.5:2.
4. a kind of magnetic fluorine ion absorber as claimed in claim 1, is characterized in that preparing Fe 3o 4@ZrO 2-CeO 2time, Fe used 3o 4quality and ZrOCl 28H 2o adds Ce (NO 3) 36H 2the quality of O and ratio be 1:5 to 1:10.
5. a preparation method for magnetic fluorine ion absorber as claimed in claim 1, is characterized in that comprising the steps:
(1) with hydro-thermal method to nanometer Fe 3o 4surface is with SiO 2modify the Fe having modified 3o 4, P123 and MgSO 4be dissolved in deionized water, then add 28% concentrated ammonia liquor and ethanol, ultrasonic dispersion, stirs;
(2) by ZrOCl 28H 2o and Ce (NO 3) 36H 2o is added in above-mentioned solution, stirs, and gained solid is separated with magnet, washing, and after refluxing with apparatus,Soxhlet's with acetone, gained solid is Fe 3o 4@ZrO 2-CeO 2, leaned on Magnetic Isolation, washing, dry;
(3) by Fe 3o 4@ZrO 2-CeO 2be placed in beaker, add the lanthanum nitrate of 1 mol/L, mix, stir after a period of time, by oxalic acid wiring solution-forming soluble in water, then oxalic acid solution is slowly added drop-wise in above-mentioned beaker, stir, finally with magnet, collect product, washing, dries.
CN201410436425.7A 2014-09-01 2014-09-01 A kind of magnetic fluorine ion absorber and preparation method thereof Expired - Fee Related CN104148004B (en)

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Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105268445A (en) * 2015-10-09 2016-01-27 合肥学院 Preparation method of Fe-Al-Ce-ZrO2 catalytic material
CN105289627A (en) * 2015-10-09 2016-02-03 合肥学院 Preparation method of Fe-Ce-ZrO2 catalysis material
CN105854783A (en) * 2016-05-20 2016-08-17 兰州交通大学 Instantly regenerated magnetic filter material for removing nitrogen and phosphorus and preparation method of instantly regenerated magnetic filter material
CN107497394A (en) * 2017-07-19 2017-12-22 南昌航空大学 A kind of Fe Mg La tri compound fluorine ion absorbers and preparation method thereof

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CN1954906A (en) * 2005-10-28 2007-05-02 中国科学院生态环境研究中心 Compound metal oxide de-fluorine sorbent
CN101811020A (en) * 2010-03-22 2010-08-25 南昌航空大学 Method for preparing Fe3O4@ZrO(OH)2 magnetic nano-adsorbing material for high-efficient fluoride removal from drinking water
CN101966445A (en) * 2010-08-30 2011-02-09 南昌航空大学 Magnetism-based nanocomposite for simultaneously removing arsenic and fluorine and application method thereof

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CN101811020A (en) * 2010-03-22 2010-08-25 南昌航空大学 Method for preparing Fe3O4@ZrO(OH)2 magnetic nano-adsorbing material for high-efficient fluoride removal from drinking water
CN101966445A (en) * 2010-08-30 2011-02-09 南昌航空大学 Magnetism-based nanocomposite for simultaneously removing arsenic and fluorine and application method thereof

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Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105268445A (en) * 2015-10-09 2016-01-27 合肥学院 Preparation method of Fe-Al-Ce-ZrO2 catalytic material
CN105289627A (en) * 2015-10-09 2016-02-03 合肥学院 Preparation method of Fe-Ce-ZrO2 catalysis material
CN105854783A (en) * 2016-05-20 2016-08-17 兰州交通大学 Instantly regenerated magnetic filter material for removing nitrogen and phosphorus and preparation method of instantly regenerated magnetic filter material
CN107497394A (en) * 2017-07-19 2017-12-22 南昌航空大学 A kind of Fe Mg La tri compound fluorine ion absorbers and preparation method thereof
CN107497394B (en) * 2017-07-19 2019-10-15 南昌航空大学 A kind of Fe-Mg-La tri compound fluorine ion absorber and preparation method thereof

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