CN110449142A - A kind of magnetic silica porous adsorbent and its preparation method and application - Google Patents

A kind of magnetic silica porous adsorbent and its preparation method and application Download PDF

Info

Publication number
CN110449142A
CN110449142A CN201910701960.3A CN201910701960A CN110449142A CN 110449142 A CN110449142 A CN 110449142A CN 201910701960 A CN201910701960 A CN 201910701960A CN 110449142 A CN110449142 A CN 110449142A
Authority
CN
China
Prior art keywords
preparation
magnetic silica
powder
silica porous
adsorbent
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
CN201910701960.3A
Other languages
Chinese (zh)
Other versions
CN110449142B (en
Inventor
汤兵
叶建文
宾丽英
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Guangdong University of Technology
Original Assignee
Guangdong University of Technology
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Guangdong University of Technology filed Critical Guangdong University of Technology
Priority to CN201910701960.3A priority Critical patent/CN110449142B/en
Publication of CN110449142A publication Critical patent/CN110449142A/en
Application granted granted Critical
Publication of CN110449142B publication Critical patent/CN110449142B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • 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
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/28Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties
    • B01J20/28002Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties characterised by their physical properties
    • B01J20/28009Magnetic properties
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/28Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties
    • B01J20/28054Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties characterised by their surface properties or porosity
    • 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
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/308Dyes; Colorants; Fluorescent agents

Landscapes

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

Abstract

The invention discloses a kind of magnetic silica porous adsorbents and its preparation method and application.The preparation of magnetic silica porous adsorbent includes the following steps: to mix SiO 2 powder and ferric ion solutions, 60~80 DEG C of hot alkaline solution is added, pH is adjusted, is sufficiently down to room temperature ageing, washing to neutrality after reaction, drying and grinding obtains magnetic silica porous adsorbent.The preparation method of magnetic silica porous adsorbent of the invention, using inorganic silicon source SiO 2 powder as raw material, it is not only cheap and easy to get, and asepsis environment-protecting, it is generated in preparation process without related organic liquid waste, it is environmental-friendly, using with surface deposition, cryogenic conditions synthesize in next step, and the reaction time is short, preparation process less energy consumption, it is at low cost.Magnetic silica porous adsorbent has good selectivity, and the maximal absorptive capacity to methylene blue is 121.23mg/g, to the maximal absorptive capacity 163.52mg/g of malachite green.

Description

A kind of magnetic silica porous adsorbent and its preparation method and application
Technical field
The present invention relates to techniques of Dyeing Wastewater Treatment fields, more particularly, to a kind of porous absorption of magnetic silica Agent and its preparation method and application.
Background technique
To water pollution control, more stringent requirements are proposed for the promulgation of " ten, water ", and industrial wastewater is as difficult to deal with one Class waste water is constantly subjected to pay close attention to, and dyeing waste water is the higher a kind of waste water of accounting in industrial wastewater discharge total amount, printing and dyeing Waste water organic concentrations are high, and coloration is big, and chemical property is stablized, difficult biochemical, are a kind of industrial wastewaters that processing difficulty is big.Printing and dyeing are useless Water is after Physiochemical and biochemical is handled, and wherein pollution index substantially reduces, and can largely reach discharge standard, but as standard is arranged The raising put, current processing method technology realize that this target is increasingly difficult to.Absorption method is in numerous technologies because of operation letter Single, at low cost, high-efficient to be favored, in absorption method, the selection of adsorbent material is the most key, therefore selects one kind Efficiently, selectivity is good, and inexpensive adsorbent material is to determine to adsorb successful deciding factor.Magnetic material has magnetic strong, easy The advantages that separating, be reusable, but magnetic material adsorption effect and adsorptive selectivity are poor.Silica is wide on earth It is general there is, inexpensive easily to take, and silica acid and alkali-resistance, stability is high, by silica and magnetic material it is compound be absorption The hot spot in investigation of materials field.The some new methods for preparing magnetic silica composite material developed in recent years have template, Sol-gal process, reverse microemulsion process etc., the preparation of these methods is more many and diverse, and the time is long and can all use certain organic molten Agent, this may bring secondary pollution to environment.For example, CN107583599A discloses a kind of monodisperse mesoporous silica Preparation, application and the regeneration method of adsorbent are reacted and post-treated obtain single point by CTAB, THEED and TEOS Mesoporous silicon oxide adsorbent is dissipated, the addition of organic substance causes the discharge of organic liquid waste in preparation process, forms secondary dirt Dye.This field is it is contemplated that a kind of environmental-friendly be easily-synthesized and the preparation of the silica magnetic adsorbent material of efficient absorption Method.
Summary of the invention
The technical problem to be solved by the present invention is to overcome existing silica magnetic adsorbent material preparation process to be easy to produce It is porous to provide a kind of magnetic silica for secondary pollution, adsorption treatment poor selectivity, adsorption efficiency not high defect and deficiency The preparation method of adsorbent.
Another object of the present invention is to provide the magnetic silica porous adsorbents that the above method is prepared.
Another object of the present invention is to provide a kind of magnetic silica porous adsorbents in dyeing waste water adsorption treatment In application.
Above-mentioned purpose of the present invention is achieved through the following technical solutions:
A kind of preparation method of magnetic silica porous adsorbent, includes the following steps: SiO 2 powder and iron Solion mixing, is added 60~80 DEG C of hot alkaline solution, adjusts pH to 10.00~12.00, and it is old to be down to room temperature after point reaction Change washing to neutrality, drying and grinding obtains magnetic silica porous adsorbent,
Wherein ferric iron and ferrous molar ratio are 1.8~2.0:1, SiO 2 powder and three in ferric ion solutions The molar ratio of valence iron is 1~3:1, and reaction temperature is 60~80 DEG C, 60~120min of reaction time.
PH value range and reaction temperature of the invention not only influences the generation of reaction, has an effect on reaction and speed occurs.
The present invention using SiO 2 powder as preparation raw material, be as inorganic silicon source SiO 2 powder it is nontoxic, Raw material that is cheap and being easy acquisition.The present invention uses surface deposition, single step reaction, that is, synthesizing magnetic porous silica simultaneously High-efficiency adsorbent, without reference to organic solvent in reaction process, reaction process carries out at low temperature, and the reaction time is short, preparation Process less energy consumption, advantage at low cost and environmentally friendly.Meanwhile magnetic silica porous high-efficiency adsorbent tool prepared by the present invention It is magnetic, can be quickly separated by solid-liquid separation using magnetic field, the material after adsorbing dyestuff can use the acid desorption of low concentration, repeat Utilization rate is high.
It is wherein preferably added to thermokalite and ferric molar ratio is 8~9:1.
Preferably, the SiO 2 powder and ferric molar ratio are 2~3:1.
Preferably, the pH is adjusted to 11~12.
It is highly preferred that the ferric iron and ferrous molar ratio are 1.8:1, SiO 2 powder rubs with ferric , than being adjusted to 11 for 2:1, pH, reaction temperature is 60 DEG C for you.
It is same it is highly preferred that the ferric iron and ferrous molar ratio are 2:1, SiO 2 powder with it is ferric Molar ratio is 3:1, and pH is adjusted to 12, and reaction temperature is 80 DEG C.
Preferably, the digestion time is 1~3h.Preferably 1h.
The magnetic silica porous adsorbent that the present invention also protects the preparation method to be prepared.
Application of the magnetic silica porous adsorbent in the Adsorption dyeing waste water dye of positive ion is also at this Within the protection scope of invention.
The dye of positive ion of the preferred Adsorption of magnetic silica porous adsorbent is methylene blue and malachite It is green.
Compared with prior art, the beneficial effects of the present invention are:
(1) the present invention provides a kind of preparation methods of magnetic silica porous adsorbent, using inorganic silicon source dioxy SiClx powder is not only cheap and easy to get as raw material, and asepsis environment-protecting, generates in preparation process without related organic liquid waste, environment friend It is good;
(2) preparation method of magnetic silica porous adsorbent of the invention, which uses, uses surface deposition, cryogenic conditions It synthesizes in next step, the reaction time is short, preparation process less energy consumption, at low cost;
(3) magnetic silica porous adsorbent of the invention has good selectivity, to the dye of positive ion have compared with High adsorption capacity, the maximal absorptive capacity to methylene blue is 121.23mg/g, to the maximal absorptive capacity of malachite green 163.52mg/g。
Specific embodiment
The present invention is further illustrated With reference to embodiment, but embodiment does not appoint the present invention The restriction of what form.Unless otherwise indicated, source chemicals used in the embodiment of the present invention are the source chemicals routinely bought.
Embodiment 1
A kind of preparation method of magnetic silica porous adsorbent, includes the following steps:
(1) 2.00g (0.005mol) Fe is weighed respectively2(SO4)3, 1.20g (0.02mol) SiO 2 powder and 1.40g (0.005mol)FeSO4·7H2O, molar concentration rate Fe3+:Fe2+:SiO2=2:1:4.First by Fe2(SO4)3And silica Powder is added in 100ml deionized water, ultrasonic disperse 10min, then magnetic agitation, to being completely dissolved, whipping temp is 60 DEG C, so Afterwards plus FeSO4·7H2O stirring a few minutes make ferrous ion be completely dissolved to obtain mixed solution.
(2) sodium hydroxide 1.60g is weighed, is dissolved in 300ml deionized water, temperature is controlled at 60 DEG C, as reaction Aqueous slkali.
(3) mixed solution in 1 step is slowly added to in the aqueous slkali in 2 steps, mixed solution has been added subsequent Continuous stirring adjusts pH to 11, and temperature is controlled at 60 DEG C, reacted 120 minutes by heating, stops heating, and ageing is washed after 1 hour Filtering to solution ph is neutrality, and air drying is ground after 12 hours up to Fe in a vacuum drying oven3+:SiO2The magnetic of=1:2 Property porous silica high-efficiency adsorbent.
The fellatio of the powder porous high-efficiency adsorbent treatment of laboratory simulation of magnetic silica made from Application Example 1 Ionic dye waste water measures its absorption property to dyestuff.Prepare the simulated wastewater that dye solution is 10~100mg/L, waste water Sample initial pH value is 6.00~7.00.When experiment, 50mg adsorbent, room temperature, revolving speed 100~150 are added in every 100mL waste water Under the conditions of rev/min, after vibrating 2h, Magneto separate takes 2~3mL supernatant, using residual in ultraviolet specrophotometer measurement solution The dyes concentration that stays simultaneously calculates adsorption capacity, and calculation formula is as follows:
In formula: the adsorption capacity of dyestuff, mg/g when qe is balance;V is wastewater volume, L;C0 is dyestuff initial concentration, mg/L;Ce is the equilibrium concentration of dyestuff, mg/L;M is the quality of adsorbent, g.
Experimental result indicates, at 25 DEG C, adsorbent is 115.20mg/g, device to hole to methylene blue maximum adsorption capacity Sparrow malachite green maximum adsorption capacity is 151.50mg/g.
Embodiment 2
A kind of preparation method of magnetic silica porous adsorbent, includes the following steps:
(1) 2.00g (0.005mol) Fe is weighed respectively2(SO4)3, 1.20g (0.02mol) SiO 2 powder and 1.55g (0.0055mol)FeSO4·7H2O, molar concentration rate Fe3+:Fe2+:SiO2=1.8:1:3.6.First by Fe2(SO4)3With two Silicon oxide powder is added in 100ml deionized water, ultrasonic disperse 10min, then magnetic agitation, to being completely dissolved, whipping temp is 60 DEG C, FeSO is then added4·7H2O stirring a few minutes make ferrous ion be completely dissolved to obtain mixed solution.
(2) sodium hydroxide 1.6g is weighed, is dissolved in 300ml deionized water, temperature is controlled at 60 DEG C, as reaction Aqueous slkali.
(3) mixed solution in 1 step is slowly added to in the aqueous slkali in 2 steps, mixed solution has been added subsequent Continuous stirring adjusts pH to 11, and temperature is controlled at 60 DEG C, reacted 120 minutes by heating, stops heating, and ageing is washed after 1 hour Filtering to solution ph is neutrality, and air drying grinds porous up to magnetic silica in a vacuum drying oven after 12 hours High-efficiency adsorbent.
The fellatio of the powder porous high-efficiency adsorbent treatment of laboratory simulation of magnetic silica made from Application Example 2 Ionic dye waste water measures its absorption property to dyestuff.Prepare the simulated wastewater that dye solution is 10-100mg/L, waste water Sample initial pH value is 6.00~7.00.When experiment, 50mg adsorbent, room temperature, revolving speed 100~150 are added in every 100mL waste water Under the conditions of rev/min, after vibrating 2h, Magneto separate takes 2~3mL supernatant, using residual in ultraviolet specrophotometer measurement solution The dyes concentration that stays simultaneously calculates adsorption capacity, and at 25 DEG C, adsorbent is to methylene blue maximum adsorption capacity 121.23mg/g is 163.52mg/g to malachite green maximum adsorption capacity.
Embodiment 3
A kind of preparation method of magnetic silica porous adsorbent, includes the following steps:
(1) Fe is weighed respectively2(SO4)3, SiO 2 powder and FeSO4·7H2O, molar concentration rate Fe3+:Fe2+: SiO2=2:1:3.First by Fe2(SO4)3It is added in 100ml deionized water with SiO 2 powder, ultrasonic disperse 10min, then magnetic Power is stirred to being completely dissolved, and whipping temp is 70 DEG C, and FeSO is then added4·7 H2O stirring a few minutes keep ferrous ion complete Dissolution obtains mixed solution.
(2) sodium hydroxide 1.6g is weighed, is dissolved in 300ml deionized water, temperature is controlled at 60 DEG C, as reaction Aqueous slkali.
(3) mixed solution in 1 step is slowly added to in the aqueous slkali in 2 steps, mixed solution has been added subsequent Continuous stirring, heating adjust pH to 11, and temperature is controlled at 70 DEG C, is reacted 120 minutes, stop heating, and ageing is washed after 1 hour Filtering to solution ph is neutrality, and air drying grinds porous up to magnetic silica in a vacuum drying oven after 12 hours High-efficiency adsorbent.
The fellatio of the powder porous high-efficiency adsorbent treatment of laboratory simulation of magnetic silica made from Application Example 3 Ionic dye waste water measures its absorption property to dyestuff.Prepare the simulated wastewater that dye solution is 10-100mg/L, waste water Sample initial pH value is 6.00~7.00.When experiment, 50mg adsorbent, room temperature, revolving speed 100~150 are added in every 100mL waste water Under the conditions of rev/min, after vibrating 2h, Magneto separate takes 2~3mL supernatant, using residual in ultraviolet specrophotometer measurement solution The dyes concentration that stays simultaneously calculates adsorption capacity, and at 25 DEG C, adsorbent is to methylene blue maximum adsorption capacity 108.61mg/g is 141.30mg/g to malachite green maximum adsorption capacity.
Embodiment 4
A kind of preparation method of magnetic silica porous adsorbent, includes the following steps:
(1) Fe is weighed respectively2(SO4)3, SiO 2 powder and FeSO4·7H2O, molar concentration rate Fe3+:Fe2+: SiO2=2:1:6.First by Fe2(SO4)3It is added in 100ml deionized water with SiO 2 powder, ultrasonic disperse 10min, then magnetic Power is stirred to being completely dissolved, and whipping temp is 80 DEG C, and FeSO is then added4·7 H2O stirring a few minutes keep ferrous ion complete Dissolution obtains mixed solution.
(2) sodium hydroxide 1.6g is weighed, is dissolved in 300ml deionized water, temperature is controlled at 60 DEG C, as reaction Aqueous slkali.
(3) mixed solution in 1 step is slowly added to in the aqueous slkali in 2 steps, mixed solution has been added subsequent Continuous stirring, heating adjust pH to 12, and temperature is controlled at 80 DEG C, is reacted 120 minutes, stop heating, and ageing is washed after 1 hour Filtering to solution ph is neutrality, and air drying grinds porous up to magnetic silica in a vacuum drying oven after 12 hours High-efficiency adsorbent.
The fellatio of the powder porous high-efficiency adsorbent treatment of laboratory simulation of magnetic silica made from Application Example 3 Ionic dye waste water measures its absorption property to dyestuff.Prepare the simulated wastewater that dye solution is 10-100mg/L, waste water Sample initial pH value is 6.00~7.00.When experiment, 50mg adsorbent, room temperature, revolving speed 100~150 are added in every 100mL waste water Under the conditions of rev/min, after vibrating 2h, Magneto separate takes 2~3mL supernatant, using residual in ultraviolet specrophotometer measurement solution The dyes concentration that stays simultaneously calculates adsorption capacity, and at 25 DEG C, adsorbent is to methylene blue maximum adsorption capacity 116.97mg/g is 155.06mg/g to malachite green maximum adsorption capacity.
Embodiment 5
A kind of preparation method of magnetic silica porous adsorbent, includes the following steps:
(1) Fe is weighed respectively2(SO4)3, SiO 2 powder and FeSO4·7H2O, molar concentration rate Fe3+:Fe2+: SiO2=2:1:2.First by Fe2(SO4)3It is added in 100ml deionized water with SiO 2 powder, ultrasonic disperse 10min, then magnetic Power is stirred to being completely dissolved, and whipping temp is 60 DEG C, and FeSO is then added4·7 H2O stirring a few minutes keep ferrous ion complete Dissolution obtains mixed solution.
(2) sodium hydroxide 1.6g is weighed, is dissolved in 300ml deionized water, temperature is controlled at 60 DEG C, as reaction Aqueous slkali.
(3) mixed solution in 1 step is slowly added to in the aqueous slkali in 2 steps, mixed solution has been added subsequent Continuous stirring, heating adjust pH to 10, and temperature is controlled at 60 DEG C, is reacted 120 minutes, stop heating, and ageing is washed after 1 hour Filtering to solution ph is neutrality, and air drying grinds porous up to magnetic silica in a vacuum drying oven after 12 hours High-efficiency adsorbent.
The fellatio of the powder porous high-efficiency adsorbent treatment of laboratory simulation of magnetic silica made from Application Example 3 Ionic dye waste water measures its absorption property to dyestuff.Prepare the simulated wastewater that dye solution is 10-100mg/L, waste water Sample initial pH value is 6.00~7.00.When experiment, 50mg adsorbent, room temperature, revolving speed 100~150 are added in every 100mL waste water Under the conditions of rev/min, after vibrating 2h, Magneto separate takes 2~3mL supernatant, using residual in ultraviolet specrophotometer measurement solution The dyes concentration that stays simultaneously calculates adsorption capacity, and at 25 DEG C, adsorbent is to methylene blue maximum adsorption capacity 96.59mg/g is 114.85mg/g to malachite green maximum adsorption capacity.
Embodiment 6
A kind of preparation method of magnetic silica porous adsorbent, includes the following steps:
(1) Fe is weighed respectively2(SO4)3, SiO 2 powder and FeSO4·7H2O, molar concentration rate Fe3+:Fe2+: SiO2=1.8:1:4.5.First by Fe2(SO4)3It is added in 100ml deionized water with SiO 2 powder, ultrasonic disperse 10min, For magnetic agitation to being completely dissolved, whipping temp is 60 DEG C again, and FeSO is then added4·7 H2O stirring a few minutes make ferrous ion It is completely dissolved to obtain mixed solution.
(2) sodium hydroxide 1.6g is weighed, is dissolved in 300ml deionized water, temperature is controlled at 60 DEG C, as reaction Aqueous slkali.
(3) mixed solution in 1 step is slowly added to in the aqueous slkali in 2 steps, mixed solution has been added subsequent Continuous stirring, heating adjust pH to 11, and temperature is controlled at 60 DEG C, is reacted 120 minutes, stop heating, and ageing is washed after 1 hour Filtering to solution ph is neutrality, and air drying grinds porous up to magnetic silica in a vacuum drying oven after 12 hours High-efficiency adsorbent.
The fellatio of the powder porous high-efficiency adsorbent treatment of laboratory simulation of magnetic silica made from Application Example 3 Ionic dye waste water measures its absorption property to dyestuff.Prepare the simulated wastewater that dye solution is 10-100mg/L, waste water Sample initial pH value is 6.00~7.00.When experiment, 50mg adsorbent, room temperature, revolving speed 100~150 are added in every 100mL waste water Under the conditions of rev/min, after vibrating 2h, Magneto separate takes 2~3mL supernatant, using residual in ultraviolet specrophotometer measurement solution The dyes concentration that stays simultaneously calculates adsorption capacity, and at 25 DEG C, adsorbent is to methylene blue maximum adsorption capacity 114.50mg/g is 138.54mg/g to malachite green maximum adsorption capacity.
Above-described embodiment illustrates that preparation process of the present invention is easy, environmental protection, at low cost, the porous height of gained magnetic silica It is good to Adsorption dye of positive ion effect to imitate adsorbent, adsorption capacity is high, is a kind of efficient absorption for removing dyeing waste water Agent has biggish use value in the market.
Comparative example 1
A kind of preparation method of magnetic silica porous adsorbent, includes the following steps:
(1) 2.00g (0.005mol) Fe is weighed respectively2(SO4)3, 1.20g (0.02mol) SiO 2 powder and 1.40g (0.005mol)FeSO4·7H2O, molar concentration rate Fe3+:Fe2+:SiO2=2:1:4.First by Fe2(SO4)3And silica Powder is added in 100ml deionized water, ultrasonic disperse 10min, then magnetic agitation, to being completely dissolved, whipping temp is 60 DEG C, so Afterwards plus FeSO4·7H2O stirring a few minutes make ferrous ion be completely dissolved to obtain mixed solution.
(2) sodium hydroxide 1.60g is weighed, is dissolved in 300ml deionized water, temperature is controlled at 60 DEG C, as reaction Aqueous slkali.
(3) mixed solution in 1 step is slowly added to in the aqueous slkali in 2 steps, mixed solution has been added subsequent Continuous stirring adjusts pH to 9, and temperature is controlled at 60 DEG C, reacted 120 minutes by heating, stops heating, and ageing is washed after 1 hour Filtering to solution ph is neutrality, and air drying is ground after 12 hours up to Fe in a vacuum drying oven3+:SiO2The magnetic of=1:2 Property porous silica high-efficiency adsorbent.
The fellatio of the powder porous high-efficiency adsorbent treatment of laboratory simulation of magnetic silica made from Application Example 1 Ionic dye waste water measures its absorption property to dyestuff, and at 25 DEG C, adsorbent is to methylene blue maximum adsorption capacity 59.65mg/g is 62.54mg/g to malachite green maximum adsorption capacity.
Comparative example 2
A kind of preparation method of magnetic silica porous adsorbent, includes the following steps:
(1) 2.00g (0.005mol) Fe is weighed respectively2(SO4)3, 1.20g (0.02mol) SiO 2 powder and 1.40g (0.005mol)FeSO4·7H2O, molar concentration rate Fe3+:Fe2+:SiO2=2:1:4.First by Fe2(SO4)3And silica Powder is added in 100ml deionized water, ultrasonic disperse 10min, then magnetic agitation, to being completely dissolved, whipping temp is 60 DEG C, so Afterwards plus FeSO4·7H2O stirring a few minutes make ferrous ion be completely dissolved to obtain mixed solution.
(2) sodium hydroxide 1.60g is weighed, is dissolved in 300ml deionized water, temperature is controlled at 60 DEG C, as reaction Aqueous slkali.
(3) mixed solution in 1 step is slowly added to in the aqueous slkali in 2 steps, mixed solution has been added subsequent Continuous stirring adjusts pH to 13, and temperature is controlled at 60 DEG C, reacted 120 minutes by heating, stops heating, and ageing is washed after 1 hour Filtering to solution ph is neutrality, and air drying is ground after 12 hours up to Fe in a vacuum drying oven3+:SiO2The magnetic of=1:2 Property porous silica high-efficiency adsorbent.
The fellatio of the powder porous high-efficiency adsorbent treatment of laboratory simulation of magnetic silica made from Application Example 1 Ionic dye waste water measures its absorption property to dyestuff, and at 25 DEG C, adsorbent is to methylene blue maximum adsorption capacity 65.45mg/g is 72.82mg/g to malachite green maximum adsorption capacity.
Obviously, the above embodiment of the present invention be only to clearly illustrate example of the present invention, and not be pair The restriction of embodiments of the present invention.For those of ordinary skill in the art, may be used also on the basis of the above description To make other variations or changes in different ways.There is no necessity and possibility to exhaust all the enbodiments.It is all this Made any modifications, equivalent replacements, and improvements etc., should be included in the claims in the present invention within the spirit and principle of invention Protection scope within.

Claims (9)

1. a kind of preparation method of magnetic silica porous adsorbent, which comprises the steps of: by silica Powder and ferric ion solutions mixing, are added 60~80 DEG C of hot alkaline solution, adjust pH to 10.00~12.00, sufficiently drop after reaction To room temperature ageing, washing to neutrality, drying and grinding obtains magnetic silica porous adsorbent,
Wherein ferric iron and ferrous molar ratio are 1.8~2.0:1 in ferric ion solutions, SiO 2 powder with it is ferric Molar ratio is 1~3:1, and reaction temperature is 60~80 DEG C, 60~120min of reaction time.
2. preparation method as described in claim 1, which is characterized in that the SiO 2 powder is 2 with ferric molar ratio ~3:1.
3. preparation method as claimed in claim 2, which is characterized in that the pH is adjusted to 11~12.
4. preparation method as claimed in claim 3, which is characterized in that the ferric iron and ferrous molar ratio are 1.8:1, two Silicon oxide powder and ferric molar ratio are 2:1, and pH is adjusted to 11, and reaction temperature is 60 DEG C.
5. preparation method as claimed in claim 3, which is characterized in that the ferric iron and ferrous molar ratio are 2:1, dioxy SiClx powder and ferric molar ratio are 3:1, and pH is adjusted to 12, and reaction temperature is 80 DEG C.
6. the preparation method as described in Claims 1 to 5 any one, which is characterized in that the digestion time is 1~3h.
7. the magnetic silica porous adsorbent that preparation method described in Claims 1 to 5 any one is prepared.
8. the answering in the Adsorption dyeing waste water dye of positive ion of magnetic silica porous adsorbent described in claim 7 With.
9. application as claimed in claim 8, which is characterized in that the dye of positive ion is methylene blue and malachite green.
CN201910701960.3A 2019-07-31 2019-07-31 Magnetic silicon dioxide porous adsorbent and preparation method and application thereof Active CN110449142B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201910701960.3A CN110449142B (en) 2019-07-31 2019-07-31 Magnetic silicon dioxide porous adsorbent and preparation method and application thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201910701960.3A CN110449142B (en) 2019-07-31 2019-07-31 Magnetic silicon dioxide porous adsorbent and preparation method and application thereof

Publications (2)

Publication Number Publication Date
CN110449142A true CN110449142A (en) 2019-11-15
CN110449142B CN110449142B (en) 2022-04-19

Family

ID=68484301

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201910701960.3A Active CN110449142B (en) 2019-07-31 2019-07-31 Magnetic silicon dioxide porous adsorbent and preparation method and application thereof

Country Status (1)

Country Link
CN (1) CN110449142B (en)

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1506407A (en) * 2002-12-06 2004-06-23 中国科学院理化技术研究所 Composite nano silica/ferroferric oxide grain material and its prepn process
CN101499348A (en) * 2008-10-30 2009-08-05 同济大学 Hollow silicon dioxide/magnetic composite microsphere and its production method
CN106111052A (en) * 2016-06-16 2016-11-16 中国科学技术大学 CoFe2o4siO2nucleocapsid structure composite nanometer particle and its production and use

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1506407A (en) * 2002-12-06 2004-06-23 中国科学院理化技术研究所 Composite nano silica/ferroferric oxide grain material and its prepn process
CN101499348A (en) * 2008-10-30 2009-08-05 同济大学 Hollow silicon dioxide/magnetic composite microsphere and its production method
CN106111052A (en) * 2016-06-16 2016-11-16 中国科学技术大学 CoFe2o4siO2nucleocapsid structure composite nanometer particle and its production and use

Non-Patent Citations (3)

* Cited by examiner, † Cited by third party
Title
FISLI A.ET AL.: ""Preparation and Characterization of Magnetite-Silica Nano-composite as Adsorbents for Removal of Methylene Blue Dyes from Environmental Water Samples"", 《ADVANCED MATERIALS RESEARCH》 *
何奕锋等: ""纳米二氧化硅粉体的制备研究进展"", 《材料开发与应用》 *
徐泽忠等: ""SiO2微纳米空心球制备及其大容量去除亚甲基蓝"", 《淮海工学院学报(自然科学版)》 *

Also Published As

Publication number Publication date
CN110449142B (en) 2022-04-19

Similar Documents

Publication Publication Date Title
CN106975443B (en) A kind of preparation method and application of magnetic modified bentonite adsorbent
CN107096510B (en) A kind of preparation method and applications of supermolecule adsorbent
CN107638868B (en) A kind of porous carbon adsorbent and its preparation method and application
CN105396555A (en) Preparation method of mesoporous print material capable of selectively adsorbing cadmium ions
CN105218765B (en) A kind of Preparation method and use of photoresponse intelligence trace mesoporous material
CN111905690A (en) Method for preparing water body nitrogen and phosphorus removal oxygenation composite material by utilizing coal ash
CN104368313B (en) A kind of preparation for dye adsorption strontium ferrite-CMC-GO magnetic adsorbent and application
CN110813264A (en) Lanthanum modified material of hydrated calcium silicate gel and preparation method thereof
CN109092083A (en) A kind of preparation and application of ferroso-ferric oxide/regenerated cellulose magnetism forward osmosis membrane
CN108371938A (en) Mesoporous magnetic Nano iron oxide material, preparation method and applications
CN106904705A (en) A kind of efficiently recyclable acidity contains As (V) method of wastewater treatment
CN101310853B (en) Calcium adsorbing material and its preparation method
CN110102291A (en) A kind of Mn oxide/zirconia composite catalyst and the preparation method and application thereof
CN109908870A (en) A kind of novel lattice vacancy HKUST-1 adsorbent and its preparation method and application
CN104971688B (en) A kind of preparation method of nano magnetic particle adsorbent
CN104623973A (en) Modified quartz sand andmodification method thereof
CN107215944B (en) Preparation method and application of sodium alginate microcapsule loaded nano Fe-FeS composite particles
CN105688795A (en) Anionic dye adsorbent composite material as well as preparation method and application thereof
CN110449142A (en) A kind of magnetic silica porous adsorbent and its preparation method and application
CN105817211A (en) Congo red dye adsorbent, preparation and method for treating Congo red dye wastewater with same
CN114367267B (en) Mesoporous composite material and preparation method and application thereof
CN101249415A (en) Barium based adsorption material and method of preparing the same
CN102350296B (en) Preparation method of magnetic mesoporous adsorption material for cationic dye
CN107583597B (en) Preparation method and application of mesoporous iron oxyhydroxide Cr (VI) adsorbent
CN110085895A (en) A kind of fluid cell and the method using its economic benefits and social benefits processing heavy metal ions in wastewater and organic dyestuff

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant